DOCSLIB.ORG

Distribution, Habitat Use and Activity Patterns of Nocturnal Small Carnivores in the North Luangwa Valley, Zambia

Total Page：16

File Type：pdf, Size：1020Kb

Download full-text PDF Read full-text
Distribution, Habitat Use and Activity Patterns of Nocturnal Small Carnivores in the North Luangwa Valley, Zambia Distribution, habitat use and activity patterns of nocturnal small carnivores in the North Luangwa Valley, Zambia Paula A. WHITE Abstract Surveys of the diversity, distribution, habitat use and nocturnal activity patterns of small carnivores were conducted in a protected part of the North Luangwa Valley, Zambia, during three periods: dry season (September–November) 2003; dry season (Sep- seven habitats, whereas the second and third took place in two forest habitats and used only camera-traps. Camera-traps were tember–November) 2004; and wet season (May–June) 2005. The first used direct-observation and camera-trap surveys across 13set carnivoreover scented species. lures The and camera-trapsoperated nightly, operated during for 17h30–05h30. 690 trap-nights In theexposing first season, 315 frames, observations 62% of ofwhich animals contained were made an animal. while Ofdriving the animals along 2,500 photographed km (100 daylight (n = 194), hours) 68% and (n 150 km (8 night-time hours) of dirt track. These first-period surveys detected Hyaenidae, Viverridae and Felidae. Viverrids accounted for nearly half (46%) of carnivores photographed, followed by mongooses = 131) were carnivores, of 11 species in five families: Mustelidae, Herpestidae,- currence in the area. Extreme daytime temperatures constrained camera-sensor operation to nights; thus, diurnal species were (35%), hyaenas (13%), mustelids (4%) and cats (2%). No species of Canidae were camera-trapped, despite their confirmed oc under-recorded. Species-specific differences observed in visitationBdeogale times between crassicauda habitats and suggestMeller’s differences Mongoose inRhynchogale species activity mel- leripatterns.) were During photographed the second most and often third (83%), survey followedperiods combined, by viverrids camera-traps (genets Genetta recorded, 9%; 674 African photographs Civet Civettictis of five carnivore civetta, 7%) species and mustelidsin the two (Ratel forest Mellivora habitats: capensismongooses, <1%). (Bushy-tailed Within the twoMongoose forest habitats, carnivore distribution, and both the timing and amount of visitation, varied by season. The highest visitation levels were in Hill Miombo in the wet season. The changing visitation rates through the night suggest that spotlighting (a popular nocturnal carnivore survey method, rarely conducted uniformly through the night) may bias detection and thus status assessments for some species. Keywords: Bdeogale crassicauda, camera-trap, Genetta, Herpestidae, miombo woodland, Rhynchogale melleri, Viverridae, wildlife survey Distribution, utilisation de l’habitat et patrons d’activité des petits carnivores nocturnes dans la Vallée de Luangwa Nord, en Zambie Résumé La diversité, la distribution, l’utilisation de l’habitat et les patrons nocturnes d’activité des petits carnivores ont été étudiés dans une partie protégée de la Vallée de Luangwa Nord, en Zambie, lors de trois périodes: 1) saison sèche (septembre–novembre) pendant2003, 2) lessaison deuxième sèche (septembre–novembre)et troisième saisons seuls 2004, des etpièges-photos 3) saison humide ont été (mai–juin) utilisés dans 2005. deux Durant habitats la première forestiers. saison, Les appareils l’étude a été menée dans sept types d’habitats et était basée sur l’observation directe et l’utilisation de pièges photographiques, alors que- vations directes d’animaux ont été faites lors d’inventaires effectués en voiture le long de 2’500 km (100 heures à la lumière du photographiques, associés à des leurres odorants, opéraient chaque nuit de 17h30–05h30. Durant la première saison, des obser animal.jour) et Des150 animauxkm (8 heures photographiés pendant la ( nnuit) = 194), de pistes 68% (enn terre. L’étude a permis de détecter 13 espèces de carnivores. Les pièges- photos ont opéré durant l’équivalent de 690 nuits de piégeage, fournissant 315 clichés dont 62% d’entre eux contenaient un (46%) de tous les carnivores photographiés, suivis par les= 131) mangoustes étaient des (35%), carnivores les hyènes appartenant (13%), les à 11mustélidés espèces réparties(4%) et les en félins cinq familles taxonomiques: Mustelidae, Herpestidae, Hyaenidae, Viverridae, Felidae. Les viverridés représentaient presque la moitié- (2%). Aucun canidé n’a été photographié malgré la confirmation de leur présence dans la zone d’étude. En raison des tempé ratures extrêmes durant la journée, le fonctionnement du senseur des appareils photographiques a été restreint aux périodes nocturnes, si bien que les espèces diurnes étaient sous-représentées. Les différences observées au niveau de l’heure des visites- des pièges-photos suggèrent des différences interspécifiquesBdeogale dans les patronscrassicauda d’activité. et Mangouste Lors des de seconde Meller etRhynchogale troisième périodes melleri) d’étudesont été photographiés combinées, les le pièges-photos plus souvent (83%),ont permis suivis d’obtenir par les viverridés674 photographies (genettes de Genetta cinq espèces, 9%), Civette de carnivores africaine dans Civettictis les deux civetta habi, tats7%) forestiers.et les mustélidés Les mangoustes (Ratel Mellivora (Mangouste capensis à queue, <1%). touffue A l’intérieur des deux habitats forestiers, la distribution des carnivores ainsi que l’heure d’occurence et le nombre de visites ont varié de manière saisonnière. Les niveaux de visite les plus élevés ont été durantobservés la dansnuit) lepeuvent miombo biaiser collinéen la détection durant la et saison ainsi les humide. évaluations Les variations du statut dans de certaines les taux de espèces. visite durant la nuit suggèrent que les études nocturnes au phare (une méthode populaire pour recenser les carnivores nocturnes rarement conduite de façon uniforme 37 Small Carnivore Conservation , Vol. 48: 37–46, July 2013 White Mots clés: Bdeogale crassicauda, forêt de miombo, Genetta Rhyn- chogale melleri, viverridés , inventaire faunistique, mangoustes, piège-photographique, Introduction pestidae), hyaenas (Hyaenidae), civets and genets (Viverridae) and cats (Felidae) (Kingdon 1977, 1997, Ansell 1978, Skinner Many African small carnivore species are inconspicuous noc- turnal forest dwellers (Ewer 1973, Smithers 1983) that are dif- The Luangwa Valley is experiencing rapid human popula- & Smithers 1990). - Nevertheless, forest carnivores are of interest both from an sulting in environmental change (Stuart et al. 1990, Dalal-Clay- academicficult to detect: standpoint as a consequence, and in light oflittle global is known trends about prioritising them. tion growth and rural expansion (Chenje & Johnson 1994) re- environmental impacts (Greene 1988). It is often assumed that ton & Child 2003, WWF-SARPOet al. 2011), 2003). the Apart ecology from of a fewLuangwa stud byresource virtue extractionof their size, and small use withoutcarnivores adequate are less consideration prone to direct of Valley’sies that focusedsmall carnivore on larger community species (Yamazaki is unknown. 1996, The Yamazaki Luangwa & persecution than are the larger species. However, illegal trade Bwalya 1999, Anderson in bush meat and skins (e.g. Colyn et al. 1988, Ray et al. 2002, monitoring programme focused on small carnivore conserva- tion.Valley The is justpresent one studyof many therefore areas insurveyed Africa lacking carnivores a long-term by cam- conversion and deforestation are all current threats to at least era-traps and direct observations in the dry and wet seasons of someGolden small 2009, African Shepherd carnivore & Shepherd species 2010,(Crooks Dolch 2002, 2011), Kauffman land 2003–2005. It took place in an area of protected, intact habitat et al - with minimal human disturbance. Thus, its results provide a man practices threaten regional populations of small carni- starting point for future studies, especially in other regions vores. 2007, is only Dunham beginning & Gaubert to be investigated 2008). The (Colón extent 2002, to which Crooks hu within and beyond the Luangwa Valley that are experiencing 2002, Azlan 2003, Kauffman et al. 2007, Cheyne et al. 2010a, rapid human population growth, rural expansion and resultant Mathai et al. 2010, Wilting et al. 2010). The paucity of baseline anthropogenic change. data about many small carnivore species hinders assessment of impacts and development of appropriate conservation strat- Methods egies (Greene 1988, Ray et al. 2002). Camera-traps are growing in popularity as an invaluable Study area The study took place in the North Luangwa National Park (11°47′S, 32°10′E), Luangwa Valley, north-eastern Zambia, researchtool for detecting such as secretiveradio-collaring. species Increasingly, (e.g. Foresman camera-traps & Pearson south-central Africa (Fig. 1). The Luangwa Valley is a trans- 1998, Cutler & Swann 1999), replacing more invasive types of verse extension of the greater African Rift Valley system, bor- et al - dered northwest by the Muchinga Escarpment and southeast ther-Hansenare documenting 2003, first Rovero records et alof. 2006,little-known Charoo carnivores et al. 2010, in by Malawi’s Nyika Plateau. To the northeast lie Tanzania’s Cheynelittle-known et al ecosystems (Brinket al . 2002, Goldmanet al .& 2010), Win Eastern Arc Mountains. The Luangwa River arises from the and may clarify species abundance (Gerber et al. 2010). For - . 2010b, Jenks . 2010,Bdeogale Moqanaki crassicauda , a spe- ennial Mwaleshi River that originates in the Muchinga Escarp- cies previously considered rare (Taylor 1987), was among the Mafinga Mountains at about 2,400 m a.s.l. It is fed by the per example,
Load more

Recommended publications
  • The Gut Microbiota of the Egyptian Mongoose As an Early Warning Indicator of Ecosystem Health in Portugal
    International Journal of Environmental Research and Public Health Article The Gut Microbiota of the Egyptian Mongoose as an Early Warning Indicator of Ecosystem Health in Portugal Mónica V. Cunha 1,2,3,* , Teresa Albuquerque 1, Patrícia Themudo 1, Carlos Fonseca 4, Victor Bandeira 4 and Luís M. Rosalino 2,4 1 National Institute for Agrarian and Veterinary Research (INIAV, IP), Wildlife, Hunting and Biodiversity R&D Unit, 2780-157 Oeiras, Portugal; [email protected] (T.A.); [email protected] (P.T.) 2 Centre for Ecology, Evolution and Environmental Changes (cE3c), Faculdade de Ciências da Universidade de Lisboa, 1749-016 Lisboa, Portugal; [email protected] 3 Biosystems & Integrative Sciences Institute (BioISI), Faculdade de Ciências da Universidade de Lisboa, 1749-016 Lisboa, Portugal 4 Departamento de Biologia & CESAM, Universidade de Aveiro, 3810-193 Aveiro, Portugal; [email protected] (C.F.); [email protected] (V.B.) * Correspondence: [email protected]; Tel.: +351-214-403-500 Received: 1 April 2020; Accepted: 27 April 2020; Published: 29 April 2020 Abstract: The Egyptian mongoose is a carnivore mammal species that in the last decades experienced a tremendous expansion in Iberia, particularly in Portugal, mainly due to its remarkable ecological plasticity in response to land-use changes. However, this species may have a disruptive role on native communities in areas where it has recently arrived due to predation and the potential introduction of novel pathogens. We report reference information on the cultivable gut microbial landscape of widely distributed Egyptian mongoose populations (Herpestes ichneumon, n = 53) and related antimicrobial tolerance across environmental gradients.
    [Show full text]
  • Genetta Poensis, King Genet
    The IUCN Red List of Threatened Species™ ISSN 2307-8235 (online) IUCN 2008: T136435A45221269 Genetta poensis, King Genet Assessment by: Gaubert, P. & Do Linh San, E. View on www.iucnredlist.org Citation: Gaubert, P. & Do Linh San, E. 2015. Genetta poensis. The IUCN Red List of Threatened Species 2015: e.T136435A45221269. http://dx.doi.org/10.2305/IUCN.UK.2015- 4.RLTS.T136435A45221269.en 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: Genetta poensis Waterhouse, 1838 Common Name(s): • English: King Genet • French: Genette royale Taxonomic Notes: This species has been considered synonymous with Pardine Genet (Genetta pardina; e.g., Crawford- Cabral 1980, Schlawe 1981, Grubb et al.
    [Show full text]
  • First Sighting of the Giant Genet Genetta Victoriae in Rwanda
    First sighting of the Giant Genet Genetta victoriae in Rwanda Vladimir DINETS Abstract A large genet photographed in 2005 in Nyungwe National Park, Rwanda, was identified as a Giant GenetGenetta victoriae, previously known with certainty only from the Democratic Republic of Congo and the adjacent part of Uganda and never before photographed in the wild. Keywords: montane rainforest, Nyungwe National Park, spotlighting, Viverridae Première observation de la Genette Géante Genetta victoriae au Rwanda Résumé Une genette de grande taille photographiée en 2005 dans le Parc National de Nyungwe au Rwanda, est identifiée comme représentant la Genette Géante Genetta victoriae ; cette espèce n’était connue que de la République Démocratique du Congo et de la partie limitrophe de l’Ouganda, et n’avait jamais été photographiée dans la nature. Mots clés: forêt ombrophile de montagne, Parc National de Nyungwe, spotlighting, Viverridae Giant Genet Genetta victoriae Thomas, 1901 is an enigmatic car- nivoran species, currently known with certainty only from northern and eastern parts of the Democratic Republic of Congo (DRC), where it inhabits lowland and montane rainforests up to 2,000 m (Van Rompaey et al. 2008). It has been predicted to occur in Rwan- da and Uganda, but there are no confirmed observations or mu- seum specimens from outside DRC (Gaubert et al. 2006), except in Semiliki Forest in Uganda on the border with DRC (Bere 1962). A captive specimen has been photographed by Rahm (1966), but there are no photos obtained in the wild, and no published infor- mation on wild animals, except for observations by Kingdon (1977) in Uganda, which appear questionable (Schreiber et al.
    [Show full text]
  • The Yellow Mongoose Cynictis Penicillata in the Great Fish River Reserve (Eastern Cape, South Africa)
    View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by South East Academic Libraries System (SEALS) Spatio-temporal ecology of the yellow mongoose Cynictis penicillata in the Great Fish River Reserve (Eastern Cape, South Africa) By Owen Akhona Mbatyoti A dissertation submitted in fulfilment of the requirements for the degree of MASTER OF SCIENCE (ZOOLOGY) in the Faculty of Science and Agriculture at the University of Fort Hare August 2012 Supervisor: Dr Emmanuel Do Linh San DECLARATION 1. This is to declare that this dissertation entitled “Spatio-temporal ecology of the yellow mongoose Cynictis penicillata in the Great Fish River Reserve (Eastern Cape, South Africa)” is my own work and has not been previously submitted to another institute. 2. I know that plagiarism means taking and using the ideas, writings, work or inventions of another person as if they were one’s own. I know that plagiarism not only includes verbatim copying, but also extensive use of another person’s ideas without proper acknowledgement (which sometimes includes the use of quotation marks). I know that plagiarism covers this sort of material found in textual sources (e.g. books, journal articles and scientific reports) and from the Internet. 3. I acknowledge and understand that plagiarism is wrong. 4. I understand that my research must be accurately referenced. I have followed the academic rules and conventions concerning referencing, citation and the use of quotations. 5. I have not allowed, nor will I in the future allow, anyone to copy my work with the intention of passing it off as their own work.
    [Show full text]
  • CHAPTER 1: Introduction 1
    University of Pretoria etd, Wilson K A (2006) Status and distribution of cheetah outside formal conservation areas in the Thabazimbi district, Limpopo province by Kelly-Anne Wilson Submitted in partial fulfilment for the requirements for the degree Magister Scientiae in Wildlife Management Centre for Wildlife Management Faculty of Natural and Agricultural Sciences University of Pretoria Pretoria Supervisor: Prof. J. du P. Bothma Co-supervisor: Prof. G. H. Verdoorn February 2006 University of Pretoria etd, Wilson K A (2006) STATUS AND DISTRIBUTION OF CHEETAH OUTSIDE FORMAL CONSERVATION AREAS IN THE THABAZIMBI DISTRICT, LIMPOPO PROVINCE by Kelly-Anne Wilson Supervisor: Prof. Dr. J. du P. Bothma Co-supervisor: Prof. Dr. G. H. Verdoorn Centre for Wildlife Management Faculty of Natural and Agricultural Sciences University of Pretoria Magister Scientiae (Wildlife Management) ABSTRACT The current status of the cheetah Acinonyx jubatus outside formal conservation areas in South Africa is undetermined. The largest part of the cheetah population in South Africa occurs on cattle and wildlife ranches. Conflict between cheetahs and landowners is common and cheetahs are often persecuted. Cheetah management and conservation efforts are hampered as little data are available on the free-roaming cheetah population. A questionnaire survey was done in the Thabazimbi district of the Limpopo province to collect data on the status and distribution of cheetahs in the district and on the ranching practices and attitudes of landowners. By using this method, a population estimate of 42 – 63 cheetahs was obtained. Camera trapping was done at a scent-marking post to investigate the marking behaviour of cheetahs. Seven different cheetahs were identified marking at one specific tree.
    [Show full text]
  • Civettictis Civetta (Schreber, 1776)
    Civettictis civetta (Schreber, 1776) The African civet, Civettictis civetta is native to and widely distributed in Africa. It was probably introduced to Sao Tome & Principe with the weasel Mustela nivalis to control rodents. African civets occupy a range of habitats including secondary forest, woodland, bush habitats as well as aquatic habitats. They are not common in interior forest habitats but thrive in degraded and deforested areas. They have been recorded at altitudes up to 5000 m asl on Mt Kilimanjaro The Guinea Lidless Skink (Afroablepharus africana) is classified as ‘Vulnerable (VU)’ in the IUCN Red List of Threatened Species. It is restricted to three locations on the islands of Sâo Tomé, Principé, and Rolas in the Gulf of Guinea. The main threats to this species are suspected to be loss of habitat through deforestation and predation Photo credit: Brianna Hackler by introduced mammals. Introduced mammals on these islands include the African civet, Norway rat (Rattus bocagei); the Sao Tome Canary (Neospiza concolor) and the norvegicus) ship rat (Rattus rattus), House mouse (Mus Sao Tome Fiscal (Lanius newtoni) are under threat of loss musculus), Mona monkey (Cercopithecus mona) and of habitat and potential predation by introduced mammals weasel. that include the African civet, ship rat, house mouse, Mona Declining populations of three endemic and ‘Critically monkey and weasel. Feral pigs (Sus scrofa) are also present Endangered (CR)’ birds the Sao Tome Ibis (Bostrychia and could be a threat. References: IUCN 2011. IUCN Red List of Threatened Species. Version 2011.2 ISSG 2012. Global Invasive Species Database Click here to view archives of previous weeks’ species.
    [Show full text]
  • 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]
  • Mammalian Predators Appropriating the Refugia of Their Prey
    Mamm Res (2015) 60:285–292 DOI 10.1007/s13364-015-0236-y ORIGINAL PAPER When prey provide more than food: mammalian predators appropriating the refugia of their prey William J. Zielinski 1 Received: 30 September 2014 /Accepted: 20 July 2015 /Published online: 31 July 2015 # Mammal Research Institute, Polish Academy of Sciences, Białowieża, Poland (outside the USA) 2015 Abstract Some mammalian predators acquire both food and predators) may play disproportionately important roles in their shelter from their prey, by eating them and using the refugia communities. the prey construct. I searched the literature for examples of predators that exhibit this behavior and summarize their taxo- Keywords Predator–prey . Dens . Herbivore . Behavior . nomic affiliations, relative sizes, and distributions. I hypothe- Habitat . Resting . Foraging sized that size ratios of species involved in this dynamic would be near 1.0, and that most of these interactions would occur at intermediate and high latitudes. Seventeen species of Introduction Carnivorans exploited at least 23 species of herbivores as food and for their refugia. Most of them (76.4 %) were in the Mammals require food and most require shelter, either to pro- Mustelidae; several small species of canids and a few tect them from predators or from thermal stress. Carnivorous herpestids were exceptions. Surprisingly, the average mammals are unique in that they subsist on mobile food predator/prey weight ratio was 10.51, but few species of pred- sources which, particularly if these sources are vertebrates, ators were more than ten times the weight of the prey whose may build their own refuges to help regulate their body tem- refugia they exploit.
    [Show full text]
  • Ecology of the Small Indian Mongoose (Herpestes Auropunctatus) in North America
    University of Nebraska - Lincoln DigitalCommons@University of Nebraska - Lincoln USDA National Wildlife Research Center - Staff U.S. Department of Agriculture: Animal and Publications Plant Health Inspection Service 2018 Ecology of the Small Indian Mongoose (Herpestes auropunctatus) in North America Are R. Berentsen USDA National Wildlife Research Center, [email protected] William C. Pitt Smithsonian Institute Robert T. Sugihara USDA/APHIS/WS/National Wildlife Research Center Follow this and additional works at: https://digitalcommons.unl.edu/icwdm_usdanwrc Part of the Life Sciences Commons Berentsen, Are R.; Pitt, William C.; and Sugihara, Robert T., "Ecology of the Small Indian Mongoose (Herpestes auropunctatus) in North America" (2018). USDA National Wildlife Research Center - Staff Publications. 2034. https://digitalcommons.unl.edu/icwdm_usdanwrc/2034 This Article is brought to you for free and open access by the U.S. Department of Agriculture: Animal and Plant Health Inspection Service at DigitalCommons@University of Nebraska - Lincoln. It has been accepted for inclusion in USDA National Wildlife Research Center - Staff Publications by an authorized administrator of DigitalCommons@University of Nebraska - Lincoln. U.S. Department of Agriculture U.S. Government Publication Animal and Plant Health Inspection Service Wildlife Services Ecology of the Small 12 Indian Mongoose (Herpestes auropunctatus) in North America Are R. Berentsen, William C. Pitt, and Robert T. Sugihara CONTENTS General Ecology and Distribution.........................................................................
    [Show full text]
  • Genetta Cristata, Crested Genet
    The IUCN Red List of Threatened Species™ ISSN 2307-8235 (online) IUCN 2008: T8998A45198406 Genetta cristata, Crested Genet Assessment by: Gaubert, P., Angelici, F.M. & Do Linh San, E. View on www.iucnredlist.org Citation: Gaubert, P., Angelici, F.M. & Do Linh San, E. 2015. Genetta cristata. The IUCN Red List of Threatened Species 2015: e.T8998A45198406. http://dx.doi.org/10.2305/IUCN.UK.2015- 4.RLTS.T8998A45198406.en 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: Genetta cristata Hayman in Sanborn, 1940 Common Name(s): • English: Crested Genet, Crested Servaline Genet • French: Genette servaline à crête Taxonomic Notes: Genetta cristata was originally described as a subspecies of the Servaline Genet G.
    [Show full text]
  • GREVY's ZEBRA Equus Grevyi Swahili Name
    Porini Camps Mammal Guide By Rustom Framjee Preface This mammal guide provides some interesting facts about the mammals that are seen by guests staying at Porini Camps. In addition, there are many species of birds and reptiles which are listed separately from this guide. Many visitors are surprised at the wealth of wildlife and how close you can get to the animals without disturbing them. Because the camps operate on a low tourist density basis (one tent per 700 acres) the wildlife is not ‘crowded’ by many vehicles and you can see them in a natural state - hunting, socialising, playing, giving birth and fighting to defend their territories. Some are more difficult to see than others, and some can only be seen when you go on a night drive. All Porini camps are unfenced and located in game rich areas and you will see much wildlife even in and around the camps. The Maasai guides who accompany you on all game drives and walks are very well trained and qualified professional guides. They are passionate and enthusiastic about their land and its wildlife and really want to show you as much as they can. They have a wealth of knowledge and you are encouraged to ask them more about what you see. They know many of the animals individually and can tell you stories about them. If you are particularly interested in something, let them know and they will try to help you see it. While some facts and figures are from some of the references listed, the bulk of information in this guide has come from the knowledge of guides and camp staff.
    [Show full text]
  • The 2008 IUCN Red Listings of the World's Small Carnivores
    The 2008 IUCN red listings of the world’s small carnivores Jan SCHIPPER¹*, Michael HOFFMANN¹, J. W. DUCKWORTH² and James CONROY³ Abstract The global conservation status of all the world’s mammals was assessed for the 2008 IUCN Red List. Of the 165 species of small carni- vores recognised during the process, two are Extinct (EX), one is Critically Endangered (CR), ten are Endangered (EN), 22 Vulnerable (VU), ten Near Threatened (NT), 15 Data Deficient (DD) and 105 Least Concern. Thus, 22% of the species for which a category was assigned other than DD were assessed as threatened (i.e. CR, EN or VU), as against 25% for mammals as a whole. Among otters, seven (58%) of the 12 species for which a category was assigned were identified as threatened. This reflects their attachment to rivers and other waterbodies, and heavy trade-driven hunting. The IUCN Red List species accounts are living documents to be updated annually, and further information to refine listings is welcome. Keywords: conservation status, Critically Endangered, Data Deficient, Endangered, Extinct, global threat listing, Least Concern, Near Threatened, Vulnerable Introduction dae (skunks and stink-badgers; 12), Mustelidae (weasels, martens, otters, badgers and allies; 59), Nandiniidae (African Palm-civet The IUCN Red List of Threatened Species is the most authorita- Nandinia binotata; one), Prionodontidae ([Asian] linsangs; two), tive resource currently available on the conservation status of the Procyonidae (raccoons, coatis and allies; 14), and Viverridae (civ- world’s biodiversity. In recent years, the overall number of spe- ets, including oyans [= ‘African linsangs’]; 33). The data reported cies included on the IUCN Red List has grown rapidly, largely as on herein are freely and publicly available via the 2008 IUCN Red a result of ongoing global assessment initiatives that have helped List website (www.iucnredlist.org/mammals).
    [Show full text]