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Abadgerfinbannerghatttta:An Opporttunfisttficrecordofttherattel Mellfivoracapensfis (Schreber,1776) (Mammalfia:Carnfivora:Mustte

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Abadgerfinbannerghatttta:An Opporttunfisttficrecordofttherattel Mellfivoracapensfis (Schreber,1776) (Mammalfia:Carnfivora:Mustte Journal of Threatened Taxa | www.threatenedtaxa.org | 26 May 2016 | 8(5): 8820–8823 N ote Occurrence of Ratel Mellfvora A badger fn Bannerghatta: an capensfs fs supplemented by a few opportunfstfc record of the Ratel dfsjuncfve ecologfcal evfdences of Mellfvora capensfs (Schreber, 1776 ) fndfvfduals from dfferent parts of ISSN 0974-7907 (Onlfne) (Mammalfa: Carnfvora: Mustelfdae) ISSN 0974-7893 (Prfnt) the world fndfcafng a poorly known from Karnataka, Indfa dfstrfbufon status. Though the OPEN ACCESS global populafon trend of R atels Avfnash Krfshnan 1 , Sunfl Panwar 2 , Aaranya Gayathrf 3 , remafns unknown, the specfes fs Sagarfka Phalke 4 & Dflfp Abanf Venkateshafah 5 lfsted as Least Concern due to fts wfde range of dfstrfbufon, although 1,3,4,5 A Rocha Indfa, #13, Kasserguppe vfllage, Bflwardahallf, they are consfdered to be rare and occur at low densffes Bannerghata Post, Bengaluru, Karnataka 560083, Indfa 2 Deputy Conservator of Forests, Bannerghata Nafonal Park, fn most parts (Begg et al. 2008) the threats to localfzed Karnataka Forest Department, Bengaluru, Karnataka 560083, Indfa populafon have occurred globally. 1 [email protected] (correspondfng author), 2 3 Wfthfn the boundarfes of Indfa, some sources [email protected], [email protected] , 4 [email protected], 5 [email protected] have ascertafned the presence of Ratels fn western and central Indfa (Prater 1971; Gupta et al. 2012) whfch fncludes states of Madhya Pradesh (Brander 1991), Gujarat and Rajasthan (Sharma 2013) and fn Sanctuary of Karnataka vfz.: Halagur, Hanur, Kaudallf and eastern Indfa the state of Odfsha (ORA 2011). A study Malaf Mahadeshwara Hflls Ranges. We present here the fn western Indfa also reported an average densfty of frst contemporary record of a Ratel whfch was camera 5.48 ±4.33 anfmals/100 km 2 fn summer and 6.43 ±2.79 trapped fn the protected area of Bannerghata Nafonal anfmals/100 km 2 fn wfnter fn Sarfska Tfger Reserve Park durfng the course of other research. (Gupta et al. 2012). Apart from a few occurrences Study Area: Bannerghata Nafonal Park (BNP) that were reported by Karanth (1986) fn Srfnfvasapura coverfng an area of ca. 256km 2 fs located fn the northern regfon of Kolar Dfstrfct fn 1974 and by Kumara & Sfngh most fp of Eastern Ghats fn the State of Karnataka, Indfa. (2007) fn parts of Kolar Dfstrfct durfng early 1960s and The park fs lfnear fn shape, extendfng not more than Sathanur fn 2003, and by Hussafn (1999) fn Tamfl Nadu, 5km fn wfdth and fs confguous fn the south-east wfth the dfstrfbufon status of Ratels fn the southern part of North Cauvery Wfldlffe Sanctuary (fn Tamfl Nadu) and fn the country remafns fnadequate. A recent report of the south-west wfth Cauvery Wfldlffe Sanctuary (CWLS; occurrence fn the southern Indfan state of Karnataka fn Karnataka). The forest predomfnantly comprfses of was publfshed by Gubbf et al. (2014) dfsclosfng tropfcal thorn scrub, dry and mofst decfduous forest occurrence of Ratels fn four ranges of Cauvery Wfldlffe types characterfzed by Acacfa chundra , Anogefssus DOI : htp://dx.dof.org/10.11609/jot.2587.8.5. 8820-8823 | ZooBank: urn:lsfd:zoobank.org:pub:CFAF7008-BF4B-47F9-A964-D3C880502747 Edftor: Anonymfty requested. Date of publfcafon: 26 May 2016 (onlfne & prfnt) Manuscrfpt detafls: Ms # 2587 | Recefved 27 February 2016 | Ffnal recefved 11 May 2016 | Ffnally accepted 16 May 2016 Cftafon: Krfshnan, A., S. Panwar, A. Gayathrf, S. Phalke & D.A. Venkateshafah (2016). A badger fn Bannerghata: an opportunfsfc record of the Ratel Mellfvora capensfs (Schreber, 1776 ) (Mammalfa: Carnfvora: Mustelfdae) from Karnataka, Indfa . Journal of Threatened Taxa 8(5): 8820–8823 ; htp://dx.dof.org/10.11609/ jot.2587.8.5. 8820-8823 Copyrfght: © Krfshnan et al. 2016 . Creafve Commons Atrfbufon 4.0 Internafonal Lfcense. JoTT allows unrestrfcted use of thfs arfcle fn any medfum, reproducfon and dfstrfbufon by provfdfng adequate credft to the authors and the source of publfcafon. Fundfng: The study was funded by A Rocha Indfa under the dfrectorate of Scfence and Conservafon. Conlfct of Interest: The authors declare no compefng fnterests. Acknowledgement: We would lfke to extend our sfncere thanks to the Karnataka Forest Department of Bannerghata Nafonal Park for thefr unsfnted support. We acknowledge the support of Idea Wfld (NPO) - USA for provfdfng some of the camera-trap equfpment, as part of a grant. The authors wfsh to thank Hfma Bfndu for helpfng wfth the GIS work. The frst author would lfke to thank Dr. Jeremy Lfndsell of A Rocha Internafonal, Prem Mftra, Aswath Honnavar and Surendra Varma for thefr revfews, support and encouragement. We are also grateful for an anonymous revfewer for fnputs and suggesfons on fmprovfng the qualfty of thfs manuscrfpt. 8820 Ratel in Bannerghatta National Park Krishnan et al. latifoliaand Shorea robusta (Suresh & Bhat 2000; Varma wildlife ranges of BNP viz., Bannerghatta wildlife range et al. 2009). BNP is inhabited by many faunal species and Harohalli wildlife range, in an opportunistic manner. including Asian Elephant Elephas maximus, Gaur Bos In Harohalli wildlife range, the camera had a trap cycle gaurus, Leopard Panthera pardus and Dhole Cuon of 13 days and were kept active throughout the day and alpinus (Singh 2008; Varma et al. 2009; Karikalan 2013). night and were positioned at a vertical height of 45cm. BNP, however experiences high anthropogenic pressures The camera-trap was set to record 24h a day and to take along the fringes from cattle grazing, sand-mining and three images per detection with a delay of 5s between fuel wood collection caused by approximately 130 images. The current location had a total sampling effort settlements lying just within 5km from the protected of 26 days. area boundary. Results: A camera set near the Karadikal- Methods: Two motion-triggered infra-red camera Mahadeshwara Elephant Corridor that connects traps (Bushnell HD 8MP Trail Camera) were set to record Harohalli and Anekal wildlife ranges of BNP between 15 the ranging patterns of a wild Tiger Panthera tigris that October 2015 and 10 November 2015 recorded images had been recently reported in BNP. Cameras were set of a Ratel on 02 November 2015 at 00h31 (Image 1). The along the likely travel routes of the Tiger in two of the age and sex of this individual could not be determined. Figure 1. Spatial representation of the records of Honey Badger in 2014 and 2015 in *approximate closest range distribution in CWLS obtained from Gubbi et al during January and March 2014. Karnataka Journal of Threatened Taxa | www.threatenedtaxa.org | 26 May 2016 | 8(5): 8820–8823 8821 Ratel in Bannerghatta National Park Krishnan et al. an approximate distance of 1km where concomitant cattle grazing has been reported by the local forest officials, to be intense along the trail path. Though a comparative study conducted by Gupta et al. (2012) reports that proximity to roads and villages may have a negative impact on habitat suitability for Ratels, the current documentation has been in a landscape much influenced by anthropogenic impacts. The northern and north-western margins of BNP are surrounded by highly human-dominated zones and Bangalore City lies at a distance of 22km north of the protected area, thereby warranting further field studies in this region for effective long-term conservation of the species. Though some Ratels in Africa have been reported to raid poultry from Image 1. Photographic record of a Ratel captured on a camera trap in BNP nearby villages (Begg & Begg 2002), no instances of such conflict caused by Ratels are known and forest officials have not seen the animal or recognized any evidences The same camera also captured images of Tiger, Gaur of Ratels in BNP prior to this record. Considering their and domestic cows. habitat requirements and conflict prone behaviour, Discussions: The forests of BNP are connected to the it could be a conservation concern and may warrant CWLS in the south-west which have had recent records further studies on population dynamics and foraging of Ratels (Fig. 1). This suggests that Ratels could range behaviour in this region. throughout this area and occur regularly within BNP. Although a single observation is insufficient to establish References a resident population of Ratels in BNP, it is clear that the habitat bears some of the ecological characteristics Begg, K. & C. Begg (2002). The conflict between Beekeepers and Honey Badgers in South Africa: a Western Cape Perspective. The that may be conducive. Though the vegetation of the Open Country 4 (Summer): 25–36. region is characterized by scrub and mixed deciduous Begg, K., C. Begg & A. Abramov (2008). Mellivora capensis. The IUCN forest with predominant occurrences of Anogeissus spp. Red List of Threatened Species 2008, e.T41629A10522766. www. iucnredlist.org. Downloaded on 21 November 2015; http://dx.doi. and Acacia spp., BNP has an average ground cover of org/10.2305/IUCN.UK.2008.RLTS.T41629A10522766.en. 62% (Varma et al. 2009) which may provide adequate Brander, D. (1991). Wild Animals in Central India. Natraj Publishers, microhabitats for these species, similar to another Dehradun, 276–277pp. Gubbi, S., V. Reddy, H. Nagashettihalli, R. Bhat & M.D. Madhusudan opportunistic report of an indirect evidence of Ratels in (2014). Photographic records of the Ratel Mellivora capensis such type of a habitat (Joshi & Andavan 2008). Moreover, from the southern Indian state of Karnataka. Small Carnivore BNP reports of a good diversity and occurrence of Conservation 50: 42–44. Gupta, S., K. Mondal, K. Sankar & Q. Qureshi (2012). Abundance and bamboo (Dendrocalamus spp.) thickets which could be habitat suitability model for Ratel (Mellivora capensis) in Sariska a viable shelter for these small carnivores (Vanderhaar Tiger Reserve, Western India. Wildlife Biology in Practice 8(1): 13– & Hwang 2003). Gupta et al. (2012) reports that water 22; http://dx.doi.org/10.2461/wbp.2012.8.2.
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