Ontologia
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Mangouste à queue courte

Urva brachyura(Gray, 1837)

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 brachyura.

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

Liste rouge IUCN

NT · Quasi menacéeDécroissante
Évaluation complète
Évaluation
2016 · v3.1
Altitude
01500 m
Profondeur
m
État de la populationExpert
Short-tailed Mongoose population status appears to vary between land-mass. In Borneo it is both geographically and ecologically widespread, and at least locally common (Duckworth et al. in prep.) and, particularly bearing in mind habitat use on Borneo (see 'Habitats and ecology' section), the population is evidently large. In West Malaysia, Wells (1989) traced rather few records, all from lowland forest; a pattern that has not changed. While the species still survives at one of the localities identified by Wells (1989), Krau Wildlife Reserve (Jennings et al. 2010), several camera-trap surveys (which record the species widely on Borneo; Duckworth et al. in prep.) in various other parts of the peninsula have not found it, even though the camera-trapping style successfully found Crab-eating Mongoose Herpestes urva (e.g., Kawanishi and Sunquist 2004, Hedges et al. 2013, K. Kawanishi pers. comm. 2014). Short-tailed Mongoose's occurrence on the peninsula is clearly ecologically localized (probably reflecting a restriction to lowland evergreen forest there; see 'Habitats and ecology' section). No detailed collation of Sumatran records exists. Whilst it evidently occurs widely there (Jennings and Veron 2011), it has not been found by camera-trapping in some large areas with high effort (Holden 2006, McCarthy and Fuller 2014, WCS Indonesia Programme pers. comm. 2006), although it has in others (Maddox et al. 2007, A.M. Mobrucker pers. comm. 2014).

There is no direct information available on the population trend on any land-mass; some inference can be made from habitat trends (see 'Threats' section).

Menaces identifiées(9 menaces classées CMP-IUCN)

  • 5_1_1
    Intentional use (species is the target)
    Negligible declinesMinority (<50%)Ongoing
  • 5_1_3
    Persecution/control
    Negligible declinesMajority (50-90%)Ongoing
  • 5_2_2
    Unintentional effects (species is not the target)
    Negligible declinesMinority (<50%)Ongoing
  • 5_3_3
    Unintentional effects: (subsistence/small scale) [harvest]
    Negligible declinesMinority (<50%)Ongoing
  • 5_3_4
    Unintentional effects: (large scale) [harvest]
    Negligible declinesMinority (<50%)Ongoing
  • 7_2_10
    Large dams
    Negligible declinesMinority (<50%)Ongoing
  • 2_1_4
    Scale Unknown/Unrecorded
    Slow, Significant DeclinesMajority (50-90%)Ongoing
  • 2_2_1
    Small-holder plantations
    Slow, Significant DeclinesMajority (50-90%)Ongoing
  • 2_2_2
    Agro-industry plantations
    Slow, Significant DeclinesMajority (50-90%)Ongoing
Description complète des menacesExpert
The different habitat use of this 'species' (see 'Taxonomic notes') between land-masses requires consideration of threats specific to each land-mass. There is no evidence that Short-tailed Mongoose can survive in plantations or other non-forest habitats remote from native forest in any land-mass. Similarly there is no evidence that it is hunted (as targeted quarry or as by-catch) in any land-mass at levels high enough to drive declines within remaining suitable habitat. Therefore, forest loss rates are likely to provide a reasonable indicator of population decline rates.

In Borneo the species is geographically and altitudinally widespread, and evidently occurs frequently in degraded and fragmented habitats (Duckworth et al. in prep.). While large-scale deforestation of Borneo in recent decades will have driven large declines in the Bornean population, there is no evidence of major threats within remaining suitable habitat. Some level of retributory killing as a (perceived or actual) predator of small livestock is likely.

In the Malay peninsula, the restriction to altitudes below 160 m and to native forest means that huge declines will have occurred in the latter half of the twentieth century, with the large-scale conversion of lowland forest to plantations. Rates of conversion have recently dropped considerably (because little remains to be converted outside legally protected areas), but the suitability of the present landscape to peninsular Short-tailed Mongoose is difficult to evaluate. There is no meaningful information on patch size required for viable populations, or on dispersal through habitats that cannot maintain the species. Although it is not known to be, it is quite plausible that the peninsular population is in ongoing decline and would warrant conservation attention.

The level of threat on Sumatra is unclear. Lowland forest loss on Sumatra is proceeding extremely rapidly, and if the species is tied to lowland forest there, major declines will be ongoing. However, if it has an altitudinal distribution similar to that in Borneo and if it uses anthropogenic habitats, declines in Sumatra will be much shallower. While an exhaustive presentation of Sumatran records with altitude and habitat condition remains to be conducted, those few records with precise altitude traced for this assessment were all from the lowlands and, because the species is evidently localized on the island, even in old-growth forest, it is possible that current rates and patterns of forest loss on Sumatra are causing serious reductions on the island.

Habitats préférentiels (classification IUCN)

  • 1_6Forest - Subtropical/Tropical Moist Lowland
  • 1_9Forest - Subtropical/Tropical Moist Montane
  • 1_8Forest - Subtropical/Tropical Swamp
  • 14_4Artificial/Terrestrial - Rural Gardens
  • 14_6Artificial/Terrestrial - Subtropical/Tropical Heavily Degraded Former Forest
  • 1_7Forest - Subtropical/Tropical Mangrove Vegetation Above High Tide Level
  • 3_6Shrubland - Subtropical/Tropical Moist
  • 3_7Shrubland - Subtropical/Tropical High Altitude
Mesures de conservation recommandéesExpert
Short-tailed Mongoose is protected in all of Malaysia and Indonesia, but receives little direct conservation attention. This is appropriate on Borneo, but not in West Malaysia. It has been found in many protected areas in Borneo, and several in West Malaysia and Sumatra. The most urgent conservation needs comprise:

Taxonomic clarification. Short-tailed Mongoose populations of (i) peninsular Malaysia and Sumatra and (ii) Borneo are distinct in mitochondrial DNA by a level suggestive of species divergence, and this is supported by dental differences (Veron et al. 2015). If further information shows them to be distinct species, and if the habitat use of the form on Sumatra echoes that in peninsular Malaysia, then the peninsular Malaysia / Sumatra form is a cryptic species that is probably globally threatened (in common with many other peninsula/Sumatran lowland forest obligate mammals and birds).

Habitat-use clarification for Sumatra. The extent to which Sumatran Short-tailed Mongoose uses hill and montane areas, and anthropogenic areas at any altitude, warrants priority assessment, as these attributes have a large effect on how threatened it is on the island.

Site protection in peninsular Malaysia. All evidence suggests that the peninsular Malaysian Short-tailed Mongoose, whatever its taxonomic rank, occupies a narrow and threatened range of habitats. Effective protection of old-growth forest is vital. Much of that which survives is already within protected areas, but these vary widely in their effectiveness at preventing illegal hunting and clearance.
Actions de conservation (3)Expert
  • 2_1Site/area management
  • 5_4_2National level
  • 5_4_3Sub-national level
Stress écologiques (13)Expert
  • 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
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_2Species disturbance
Priorités de recherche (5)Expert
  • 1_1Taxonomy
  • 1_2Population size, distribution & trends
  • 1_3Life history & ecology
  • 1_5Threats
  • 3_4Habitat trends
Niche IUCN globaleExpert

Royaumes biogéographiques

Indomalayan

Systèmes (terrestre/eau douce/marin)

Terrestrial
Références bibliographiques (21)Expert
  1. Duckworth, J.W. et al. in prep.. Predicted distribution of Short-tailed Mongoose <i>Herpestes brachyurus</i> in Borneo.
  2. IUCN. 2016. The IUCN Red List of Threatened Species. Version 2016-1. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 30 June 2016).
  3. 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.
  4. McCarthy, J.M. and Fuller, T.K. 2014. Records of small carnivores from Southern Sumatra. <i>Small Carnivore Conservation</i> 51: 59–63.
  5. Chutipong, W., Tantipisanuh, N., Ngoprasert, D., Lynam, A.J., Steinmetz, R., Jenks, K.E., Grassman Jr., L.I., Tewes, M., Kitamura, S., Baker, M.C., McShea, W., Bhumpakphan, N., Sukmasuang, R., Gale, G.A., Harich, F.K., Treydte, A.C., Cutter, P., Cutter, P.B., Suwanrat, S., Siripattaranukul, K., Hala-Bala Wildlife Research Station, Wildlife Research Division and Duckworth, J.W. 2014. Current distribution and conservation status of small carnivores in Thailand: a baseline review. <i>Small Carnivore Conservation</i> 51: 96–136.
  6. Hedges, L., Clements, G.R., Aziz, S.A., Yap, W., Laurance, S., Goosem, M. and Laurance, W.F. 2013. Small carnivore records from a threatened habitat linkage in Terengganu, Peninsular Malaysia. <i>Small Carnivore Conservation</i> 49: 9–14.
  7. Pacifici, M., Santini, L., Di Marco, M., Baisero, D., Francucci, L., Grottolo Marasini, G., Visconti, P. and Rondinini, C. 2013. Generation length for mammals. <i>Nature Conservation</i> 5: 87–94.
  8. Jennings, A.P. and Veron, G. 2011. Predicted distributions and ecological niches of 8 civet 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: 2261–2270.
  10. Jennings, A.P., Akbar Zubaid and Veron, G. 2010. Home ranges, movements and activity of the Short-tailed Mongoose (<i>Herpestes brachyurus</i>) on Peninsular Malaysia. <i>Mammalia</i> 74: 43–50.
  11. Maddox, T., Priatna, D., Gemita, E. and Salampessy, A. 2007. The conservation of Tigers and other wildlife in oil palm plantations. Jambi province, Sumatra, Indonesia. Zoological Society of London, London (Conservation Report 7).
  12. Holden, J. 2006. Small carnivores in central Sumatra. <i>Small Carnivore Conservation</i> 34&35: 35–38.
  13. Wilson, D.E., Helgen, K.M., Chin Sing Yun and Belden G. 2006. Small mammal survey at two sites in planted forest zone, Bintulu, Sarawak. <i>Malayan Nature Journal</i> 59: 165–187.
  14. Kawanishi, K. and Sunquist, M.E. 2004. Conservation status of tigers in a primary rainforest of Peninsular Malaysia. <i>Biological Conservation</i> 120: 329–344.
  15. Van Rompaey, H. 2000. The Short-tailed Mongoose, <i>Herpestes brachyurus</i>. <i>Small Carnivore Conservation</i> 23: 17-21.
  16. Heaney, L.R., Balete, D.S., Dollar, M.L., Alcala, A.C., Dans, A.T.L., Gonzales, P.C., Ingle, N.R., Lepiten, M.V., Oliver, W.L.R., Ong, P.S., Rickart, E.A., Tabaranza Jr., B.R. and Utzurrum, R.C.B. 1998. A synopsis of the mammalian fauna of the Philippine Islands. <i>Fieldiana: Zoology (New Series)</i> 88: 1–61.
  17. Corbet, G.B. and Hill, J.E. 1992. <i>Mammals of the Indo-Malayan Region: a Systematic Review</i>. Oxford University Press, Oxford, UK.
  18. Wells, D.R. 1989. Notes on the distribution and taxonomy of peninsular Malaysian mongooses (<i>Herpestes</i>). <i>Natural History Bulletin of the Siam Society</i> 37: 87-97.
  19. 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.
  20. Davis, D.D. 1962. Mammals of the lowland rainforest of North Borneo. <i>Bulletin of the National Museum of Singapore</i> 31: 1–29.
  21. Allen, J.A. 1910. Mammals from Palawan Island, Philippine Islands. <i>Bulletin of the American Museum of Natural History</i> 28: 13-17.
Évaluateurs & contributeurs (3)Expert
assessor
Duckworth, J.W., Mathai, J., Ross, J. & Wilting, A.
contributor
Widmann, P., Roberton, S., Gumal, M., Mo�brucker, A.M., Low, C.H.S., Jennings, A., Azlan, M.J., Hon, J., Chua, M.A.H. & Willcox, D.H.A.
evaluator
Schipper, J.

Duckworth, J.W., Mathai, J., Ross, J. & Wilting, A. 2016. Urva brachyura. The IUCN Red List of Threatened Species 2016: e.T41610A45206655. Accessed on 05 May 2026.

Traits biologiques

20 valeurs · 6 sources

Morphologie(4)

Masse adulte
1,41 kg
AnAge
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
4
AnAge
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 brachyurusGray, 1837
  • Herpestes brachyurus hoseiJentink, 1903
  • Herpestes brachyurus javanensisBechthold, 1936
  • Herpestes brachyurus sumatriusThomas, 1921
  • Herpestes hoseiJentink, 1903

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