Ontologia
Mangouste à collier

Mangouste à collier

Urva semitorquata(Gray, 1846)

NTLR Monde (IUCN)
1 photo · Licences CC (Wikimedia Commons / iNaturalist)Click pour agrandir
Pays · région · aire protégée · écorégion · biome

Graphe en cours d’indexation

Calcul du tissu écologique de Urva semitorquata.

Le graphe apparaîtra automatiquement dès que le calcul est terminé (rafraîchissement toutes les 5s).

Liste rouge IUCN

NT · Quasi menacéeDécroissante
Évaluation complète
Évaluation
2015 · v3.1
Altitude
01400 m
Profondeur
m
État de la populationExpert
Collared Mongoose populations are particularly poorly known, even compared with other Southeast Asian small carnivores. Although rising camera-trap use has increased the number of localities known to hold the species, it remains difficult to assess population size of unmarked animals based on camera-trap studies alone; the paucity of research on the species also prevents reliable quantitative estimates. This species is widespread in Borneo where it has been detected over a wide altitudinal range in a variety of habitat types. It is thought that in Borneo this species may be more common between elevations of 100 and 500 m asl (J. Ross unpublished data, J. Mathai unpublished data) and may occur less frequently in recently logged forest (J. Brodie pers. comm. 2014) and that, in general, it may occur primarily in less disturbed forest types (A. Wilting pers. comm. 2014). Encounter rates appear to be lower than the regularly camera-trapped and well-documented Short tailed Mongoose Herpestes brachyurus (J. Hon pers. comm. 2014, J. Ross pers. comm. 2014, J. Mathai pers. comm. 2014) although some camera-trap studies have found the reverse (J. Brodie pers. comm. 2014). On Sumatra, there is even less information on the population status of the species, at least in part reflecting the lower survey effort there and the lack of a record-collation process comparable to the Borneo Carnivore Symposium. While it is evidently widespread there, available data suggest a much smaller population than that on Borneo.

Menaces identifiées(11 menaces classées CMP-IUCN)

  • 1_1
    Housing & urban areas
    Negligible declinesMinority (<50%)Ongoing
  • 1_2
    Commercial & industrial areas
    Negligible declinesMinority (<50%)Ongoing
  • 2_1_1
    Shifting agriculture
    Negligible declinesMinority (<50%)Ongoing
  • 2_1_2
    Small-holder farming
    Negligible declinesMinority (<50%)Ongoing
  • 2_1_3
    Agro-industry farming
    Negligible declinesMinority (<50%)Ongoing
  • 2_2_1
    Small-holder plantations
    Negligible declinesMinority (<50%)Ongoing
  • 5_1_1
    Intentional use (species is the target)
    Negligible declinesMajority (50-90%)Ongoing
  • 5_2_2
    Unintentional effects (species is not the target)
    Negligible declinesMajority (50-90%)Ongoing
  • 5_3_3
    Unintentional effects: (subsistence/small scale) [harvest]
    Negligible declinesMajority (50-90%)Ongoing
  • 2_2_2
    Agro-industry plantations
    Slow, Significant DeclinesMajority (50-90%)Ongoing

+ 1 menaces supplémentaires

Description complète des menacesExpert
Deforestation and forest degradation in the lowland and upland forests of Borneo and Sumatra have been extensive through factors including unsustainable logging, conversion of natural forest to monoculture plantations, expansion of human settlements and forest fires. Based on the GIS exercise as part of this assessment (detailed in the section on Range Description), it is predicted that between 2000 and 2010 roughly 16% of potentially suitable land-cover classes for Collared Mongoose were lost in Borneo, and 35% in Sumatra. Although the species shows some tolerance to modified habitat and can presumably persist in selectively logged forest, there is no evidence to show that it can survive in clear-felled forest and oil palm plantations. This species’ use of secondary forest and higher elevations in Borneo, however, imply that it is not immediately threatened on the island. Another possible threat is indiscriminate hunting such as the use of snares and nets. Although it is unlikely that the species will wander into gardens and orchards of villages and get into direct conflict with people, suggesting that there will be only little targeted hunting as a pest, it is still exposed to these indiscriminate hunting methods, which occur deep within some forest-blocks in its range, due to its ground-dwelling nature.

Habitats préférentiels (classification IUCN)

  • 1_6Forest - Subtropical/Tropical Moist Lowland
  • 1_8Forest - Subtropical/Tropical Swamp
  • 1_9Forest - Subtropical/Tropical Moist Montane
  • 14_6Artificial/Terrestrial - Subtropical/Tropical Heavily Degraded Former Forest
Mesures de conservation recommandéesExpert
Collared Mongoose is not a CITES-listed species (CITES 2014) presumably because it is thought unlikely to feature in international trade. It is found in some protected areas within its range such as Pulong Tau National Park and Mulu National Park in Sarawak (Brodie et al. in prep.); Kinabalu Park (Wells et al. 2005), Crocker Range National Park (J. Ross pers. comm. 2014), and the Maliau Basin Conservation Area (Brodie and Giordano 2010) in Sabah; Sabangau National Park in Kalimantan (Cheyne et al. 2010); and Gunung Leuser National Park and Jantho Wildlife Sanctuary in Sumatra (Holden and Meijaard 2012, Pusparini and Sibarani 2014). However, it is not known how large any of these populations may be or whether any of them are viable. Possible strongholds where conservation efforts should arguably be focused have been identified (Hon et al. in prep.) although population status in these areas remains to be verified. On Malaysian Borneo, the species is listed as ‘Protected’ under the Sarawak Wild Life Protection Ordinance (1998) and the Sabah Wildlife Conservation Enactment (1997), implying limited protection. However, the species is not listed as a protected animal in Brunei under the Brunei Wild Life Protection Act (1978); neither is it protected in Indonesian Borneo or Sumatra under the Appendix of the Government of Republic of Indonesia Regulation No. 7 (1999).
Actions de conservation (8)Expert
  • 2_1Site/area management
  • 4_3Awareness & communications
  • 5_2Policies and regulations
  • 5_3Private sector standards & codes
  • 5_4_2National level
  • 5_4_3Sub-national level
  • 6_1Linked enterprises & livelihood alternatives
  • 6_3Market forces
Stress écologiques (18)Expert
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 2_1Species mortality
Priorités de recherche (6)Expert
  • 1_1Taxonomy
  • 1_2Population size, distribution & trends
  • 1_3Life history & ecology
  • 1_5Threats
  • 3_1Population trends
  • 3_4Habitat trends
Niche IUCN globaleExpert

Royaumes biogéographiques

Indomalayan

Systèmes (terrestre/eau douce/marin)

Terrestrial
Références bibliographiques (28)Expert
  1. IUCN. 2015. The IUCN Red List of Threatened Species. Version 2015-4. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 19 November 2015).
  2. Veron, G., Patou, M.L., Debruyne, R., Couloux, A., Fernandez, D.A.P., Wong, S.T., Fuchs, J. and Jennings, A.P. 2015. Systematics of the Southeast Asian mongooses (Herpestidae, Carnivora) - Solving the mystery of the elusive Collared Mongoose and Palawan mongoose. <i>Zoological Journal of the Linnean Society</i> 173: 246–248.
  3. Pusparini, W. and Sibarani, M.C. 2014. The first record of Indonesian Mountain Weasel <i>Mustela lutreolina</i> from northern Sumatra, Indonesia. <i>Small Carnivore Conservation</i> 51: 92–95.
  4. CITES. 2014. Appendices I, II and III of the Convention on International Trade in Endangered Species of Wild Fauna and Flora. Available at: <a href="http://www.cites.org/eng/app/appendices.php">http://www.cites.org/eng/app/appendices.php</a>.
  5. Holden, J. and Meijaard, E. 2012. An orange-coloured Collared Mongoose <i>Herpestes semitorquatus</i> from Aceh, Sumatra, Indonesia. <i>Small Carnivore Conservation</i> 47: 26–29.
  6. Ross, J., Gemita, E., Hearn, A.J. and Macdonald, D.W. 2012. The occurrence of reddish-orange mongooses <i>Herpestes</i> in the Greater Sundas and potential for their field confusion with Malay Weasel <i>Mustela nudipes</i>. <i>Small Carnivore Conservation</i> 46: 8–11.
  7. Samejima, H. and Semiadi, G. 2012. First record of Hose’s Civet <i>Diplogale hosei</i> from Indonesia and records of other carnivores in the Schwaner Mountains, Central Kalimantan, Indonesia. <i>Small Carnivore Conservation</i> 46: 1–7.
  8. Jennings, A.P. and Veron, G. 2011. Predicted distributions and ecological niches of 8 civets and mongoose species in Southeast Asia. <i>Journal of Mammalogy</i> 92: 316–327.
  9. Miettinen, J., Shi, C. and Liew, S.C. 2011. Deforestation rates in insular Southeast Asia between 2000 and 2010. <i>Global Change Biology</i> 17(7): 2261-2270. DOI:10.111/j.1365-2486.2011.02398.x.
  10. Mathai, J., Juat, N. and Peter, A. 2010b. Carnivore records, including updated records of the endemic Hose’s Civet <i>Diplogale hosei</i>, from a logging concession in the Upper Baram, Sarawak. <i>Sarawak Museum Journal LXVII</i> 88: 159–188.
  11. Mathai, J., Hon, J., Juat, N., Peter, A. and Gumal, M. 2010a. Small carnivores in a logging concession in the Upper Baram, Sarawak, Borneo. <i>Small Carnivore Conservation</i> 42: 1–9.
  12. Wilting, A., Samejima, H. and Mohamed, A. 2010. Diversity of Bornean viverrids and other small carnivores in Deramakot Forest, Sabah, Malaysia. <i>Small Carnivore Conservation</i> 42: 10–13.
  13. Cheyne, S.M., Husson, S.J., Chadwick, R.J. and Macdonald, D.W. 2010. Diversity and activity of small carnivores of the Sabangau Peat-swamp Forest, Indonesian Borneo. <i>Small Carnivore Conservation</i> 43: 1–7.
  14. Belden, G., Stuebing, R. and Nyegang, M. 2007. Small carnivores in mixed-use forest in Bintulu Division, Sarawak, Malaysia. <i>Small Carnivore Conservation</i> 36: 35-37.
  15. Wells, K., Bium, A. and Gabin, M. 2005. Viverrid and herpestid observations by camera and small cage trapping in the lowland rainforests on Borneo including a record of the Hose’s Civet, <i>Diplogale hosei</i>. <i>Small Carnivore Conservation</i> 32: 12–14.
  16. Wells, K.L. 2005. Impacts of rainforest logging on non-volant small mammal assemblages in Borneo. Fakultat fur Naturwissenschaften der Universitat Ulm.
  17. Shepherd, C.R., Sukumaran, J. and Wich, S.A. 2004. Open season: an analysis of the pet trade in Medan, Sumatra, 1997–2001. TRAFFIC Southeast Asia, Petaling Jaya, Selangor, Malaysia.
  18. President of the Republic of Indonesia. 1999. <i>Nomor 7 Tahun 1999 Tentang Pengawetan Jenis Tumbuhan dan Satwa</i>. Peraturan Pemerintahan Republik Indonesia.
  19. Wild Life Protection Ordinance. 1998. <i>Sarawak Wild Life Protection Ordinance 1998</i>. SFD, Kuching, Sarawak, Malaysia.
  20. Wildlife Conservation Enactment. 1997. <i>Sabah Wildlife Conservation Enactment 1997</i>. Sabah Wildlife Department, Kota Kinabalu, Sabah, Malaysia.
  21. Stuebing, R.B. and Gasis, J. 1989. A survey of small mammals within a Sabah tree plantation in Malaysia. <i>Journal of Tropical Ecology</i> 5: 203–214.
  22. Payne, J., Francis, C.M. and Phillipps, K. 1985. <i>A field guide to the mammals of Borneo</i>. The Sabah Society and WWF Malaysia, Kota Kinabalu and Kuala Lumpur, Malaysia.
  23. Wild Life Protection Act. 1978. <i>Brunei Wild Life Protection Act 1978</i>. Brunei Forest Department, Brunei.
  24. Medway, Lord. 1965. Mammals of Borneo. Field keys and an annotated checklist. <i>Journal of the Malaysan Branch of the Royal Asiatic Society</i> 36: 1–193.
  25. Davis, D.D. 1958. Mammals of the Kelabit plateau, northern Sarawak. <i>Fieldiana, Zoology</i> 39: 119–147.
  26. Robinson, H.C. and Kloss, C.B. 1919. On mammals, chiefly from the Ophir District, West Sumatra. <i>Journal of the Federated Malay States Museum</i> 7: 299–323.
  27. Jentink, F.A. 1894. On a specimen of <i>Herpestes semitorquatus</i> Gray from Sumatra. <i>Noes Lieden Museum</i> 16: 210.
  28. Jentink, F.A. 1894. On a specimen of <i>Herpestes semitorquatus</i> Gray from Sumatra. <i>Noes Lieden Museum</i> 16: 210.
Évaluateurs & contributeurs (3)Expert
assessor
Mathai, J., Hearn, A., Brodie, J., Wilting, A., Duckworth, J.W., Ross, J., Holden, J., Gemita, E. & Hon, J.
contributor
Azlan J., M., Jennings, A., Veron, G., Pratje, P.H. & Mo�brucker, A.M.
evaluator
Schipper, J.

Mathai, J., Hearn, A., Brodie, J., Wilting, A., Duckworth, J.W., Ross, J., Holden, J., Gemita, E. & Hon, J. 2015. Urva semitorquata. The IUCN Red List of Threatened Species 2015: e.T41616A45208027. Accessed on 05 May 2026.

Traits biologiques

20 valeurs · 4 sources

Morphologie(4)

Masse adulte
-999000 mg
PanTHERIA
Longueur
-999 mm
PanTHERIA
Masse naissance
-999000 mg
PanTHERIA
Masse au sevrage
-999000 mg
PanTHERIA

Cycle de vie(1)

Longévité max
-999 mois
PanTHERIA
Voir 15 traits de plus (2 catégories)

Reproduction(6)

Gestation
-999 j
PanTHERIA
Intervalle naissances
-999 j
PanTHERIA
Taille de portée
-999
PanTHERIA
Portées par an
-999
PanTHERIA
Maturité sexuelle
-999 j
PanTHERIA
Sevrage
-999 j
PanTHERIA

Écologie & habitat(9)

Fruits (%)
10 %
elton_mammals
Invertébrés (%)
30 %
elton_mammals
Nectar (%)
0 %
elton_mammals
Autre végétal (%)
0 %
elton_mammals
Charognard (%)
0 %
elton_mammals
Graines (%)
0 %
elton_mammals
Vert. ectothermes (%)
30 %
elton_mammals
Vert. endothermes (%)
20 %
elton_mammals
Poissons (%)
10 %
elton_mammals

Sources priorisées par qualité scientifique (peer-reviewed spécialisées → Wikidata fallback). Unités auto-converties, valeur max retenue en cas de mesures multiples. Méthodologie · Citations.

Répartition mondiale (heatmap GBIF)Construction en cours

0 obs · 0 cellules
Construction par partitions temporelles GBIF0%

Source : GBIF — observations agrégées par hexagones 0.2° × 0.2° (~22km). Filtre qualité : précision coordonnée < 10 km. Coloration quantile (q50/70/90/99). Fond carte : OpenFreeMap · © OpenStreetMap.

Distribution mondiale

Calcul de la distribution GBIF· ~10–60 s

Phénologie

Calcul du calendrier d'apparition· ~5–30 s

Consulter sur les bases externes

Observations & statuts

Cartographie

Bibliographie

Note nomenclaturale & synonymesExpert

Note nomenclaturale

TAXREF v18 — INPN/MNHN

Synonymes (5)— redirigent vers cette page

  • Herpestes brachyurus palawanusAllen, 1910
  • Herpestes brachyurus parvusJentink, 1895
  • Herpestes semitorquatusGray, 1846
  • Herpestes semitorquatus semitorquatusGray, 1846
  • Herpestes semitorquatus uniformisRobinson & Kloss, 1919

Sources : Catalogue of Life Cross-References (synonymes) · TAXREF v18 INPN/MNHN (commentaires FR).