
Euplère de Goudot
Eupleres goudotiiDoyère, 1835
Description
espèce de mammifères
Source : Wikidata
Graphe en cours d’indexation
Calcul du tissu écologique de Eupleres goudotii.
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Liste rouge IUCN
VU · Vulnérablecritères A2cde+3cde+4cde↘Décroissante- Évaluation
- 2016 · v3.1
- Altitude
- 0 – 1000 m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
Gerber et al. (2012) recorded Eastern Falanouc at 7% of camera-trap stations in primary forest and 31% of stations in selectively logged forest at Ranomafana National Park. The species was not found in forest fragments more than 2.5 km from intact forest.
In north-east Madagascar, camera-trap surveys of Farris (et al. in review a, pers. comm 2014) revealed a low probability of occupancy (defined as the probability that a site/forest is occupied by the species of interest while taking into account the variation in detectability of the species across the various sites) (0.31 ± SE 0.07) for Eastern Falanouc across the Masoala-Makira landscape. This included a similar probability of occupancy in non-degraded (0.24 ± SE 0.08) and degraded (0.30 ± SE 0.07) rainforest. Its occupancy had a strong positive association with bird camera-trap success, possibly an indication that large birds of the kinds that set off camera-traps are subject to similar threats (Farris and Kelly 2011, Farris et al. in review a). In addition to these similar estimates of occupancy, Eastern Falanouc was also found in all degraded, fragmented forest sites (including the Farankarina site over 5 km from contiguous forest) indicating that it might not depend upon contiguous forest.
Surveys over 2008-2013 and resulting multi-season occupancy analyses at one contiguous forest site showed that Eastern Falanouc occupancy decreased significantly from 0.79 (2008) to 0.20 (2013) (camera-trap success [number of captures divided by trap nights multiplied by 100] during this time dropped from 3.11 in 2008 to 1.09 in 2013) which resulted in a probability of local extirpation of 0.31 (0.10), while camera-trap success at an additional site remained low over the three-year period from from 2011 (0.33) to 2013 (0.25) (Z. Farris pers. comm. 2014).
Menaces identifiées(6 menaces classées CMP-IUCN)
8_1_2Named speciesRapid DeclinesWhole (>90%)Ongoing8_1_2Named speciesRapid DeclinesWhole (>90%)Ongoing8_1_2Named speciesUnknownWhole (>90%)Ongoing5_1_1Intentional use (species is the target)Slow, Significant DeclinesMajority (50-90%)Ongoing5_3_3Unintentional effects: (subsistence/small scale) [harvest]Slow, Significant DeclinesMajority (50-90%)Ongoing5_3_4Unintentional effects: (large scale) [harvest]Slow, Significant DeclinesMajority (50-90%)Ongoing
Description complète des menacesTexte détaillé évaluation IUCNExpert
This species is actively hunted for its meat by people. In north-east Madagascar, Farris et al. (in review a, pers. comm. 2014) found 28 Falanoucs reportedly consumed from 2005 to 2011 across four villages (143 households were surveyed) near the Makira Natural Park. Hunting rates were highest in non-degraded forest and were positively associated with Falanouc occupancy, meaning that hunters appear to be focusing their efforts in non-degraded forest where Falanouc is most abundant (Farris et al. in review a). Household interviews conducted by Madagasikara Voakajy (pers. comm. 2014) in the Moramanga region of eastern Madagascar in 2008-2009 suggested that 425 (28%) of 1,532 respondents interviewed in 129 villages had eaten Falanouc in the preceding year. Hunting is presumed to have increased significantly in many parts of the species's range since 2009 because of less effective governance and increased social instability following a coup d'etat.
Competition with the introduced Small Indian Civet Viverricula indica is sometimes cited as a threat, although this might not be very significant. Competition with and predation by feral cats and dogs is more likely to be an important threat. Eastern Falanouc activity overlaps with that of Small Indian Civet, revealing the potential for increased interactions and competition (Farris et al. in review b). Eastern Falanouc presence and probability of occupancy is higher at sites where cats are most active. This may be a habitat-mediated relationship; but it presumably translates into increased interactions between these two species (Farris et al. in review c). Eastern Falanouc probability of occupancy increases dramatically when dogs are not present at a site and the two occur together less than expected across the landscape, meaning Falanouc does not use sites where dogs are highly active (Farris et al. in review c); perhaps dogs kill Falanoucs.
Habitats préférentiels (classification IUCN)
1_6Forest - Subtropical/Tropical Moist Lowland
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
Actions de conservation (6)Conservation Actions Classification Scheme — IUCNExpert
2_1Site/area management2_2Invasive/problematic species control4_2Training4_3Awareness & communications5_4_2National level5_4_3Sub-national level
Stress écologiques (8)Stresses Classification — IUCNExpert
1_2Ecosystem degradation1_2Ecosystem degradation2_1Species mortality2_1Species mortality2_1Species mortality2_3_2Competition2_3_2Competition2_3_2Competition
Usage & commerce (1)Use & Trade — IUCNExpert
1Food - humansubsistance
Priorités de recherche (6)Research Needed Classification — IUCNExpert
1_3Life history & ecology1_4Harvest, use & livelihoods1_5Threats3_1Population trends3_2Harvest level trends3_4Habitat trends
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Systèmes (terrestre/eau douce/marin)
Références bibliographiques (10)Sources scientifiques de l'évaluation IUCNExpert
- Farris, Z.J., Gerber, B., Kelly, M.J., Karpanty, S., Murphy, F. and Andrianjakarivelo, V. In review b. When the carnivores roam: temporal patterns and partitioning among Madagascar’s native and exotic carnivores.
- Farris, Z.J., Golden, C., Karpanty, S., Murphy, A., Stauffer, D., Andrianjakarivelo, V., Ratelolahy, F., Holmes, C. and Kelly, M.J. In review a. Effects of poaching, micro-habitat and landscape variables, human encroachment, and exotic species on Madagascar’s endemic and exotic carnivore community across the Masoala-Makira landscape.
- Farris, Z.J., Karpanty, S., Kelly, M., Murphy, A., Ratelolahy, F. and Holmes C. In prep. c. Spatial co-occurrence and detection of endemic and exotic carnivores in Madagascar: factors impacting their interactions across the Masoala-Makira landscape.
- 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).
- Allnut, T.F., Asner, G.P., Golden, C.D. and Powell, G.V.N. 2013. Mapping recent deforestation and disturbance in northeastern Madagascar. <i>Tropical Conservation Science</i> 6: 1-15.
- Gerber, B.D., Karpanty, S.M. and Randrianantenaina, J. 2012. The impact of forest logging and fragmentation on carnivore species composition, density and occupancy in Madagascar's rainforests. <i>Oryx</i> 46: 414-422.
- Farris Z.J. and Kelly, M.J. 2011. A preliminary assessment of carnivores across the Makira Protected Area, Madagascar: results from a WCS pilot camera study. Wildlife Conservation Society, Antananarivo, Madagascar.
- Goodman, S.M. and Helgen, K.M. 2010. Species limits and distribution of the Malagasy carnivoran genus <i>Eupleres</i> (family Eupleridae). <i>Mammalia</i> 74: 177–185.
- Dollar, L. 2000. Assessing IUCN classifications of poorly-known species: Madagascar's carnivores as a case study. <i>Small Carnivore Conservation. The Newsletter and Journal of the IUCN/SSC Mustelid, Viverrid and Procyonid Specialist Group</i> 22:17-20.
- Schreiber, A., Wirth, R., Riffel, M. and Van Rompaey, H. 1989. <i>Weasels, Civets, Mongooses and their Relatives. An Action Plan for the Conservation of Mustelids and Viverrids</i>. IUCN, Gland, Switzerland.
Évaluateurs & contributeurs (3)Personnes ayant contribué à l'évaluation IUCNExpert
Hawkins, F. 2016. Eupleres goudotii. The IUCN Red List of Threatened Species 2016: e.T68336601A45204582. Accessed on 05 May 2026.
Traits biologiques
Morphologie(4)
Cycle de vie(1)
Voir 15 traits de plus (2 catégories)Replier
Reproduction(6)
Écologie & habitat(9)
Sources priorisées par qualité scientifique (peer-reviewed spécialisées → Wikidata fallback). Unités auto-converties, valeur max retenue en cas de mesures multiples. Méthodologie · Citations.
Distribution mondiale
Phénologie
Consulter sur les bases externes
Observations & statuts
Cartographie
Note nomenclaturale & synonymesDétails taxonomiques + synonymes CoLExpert
Note nomenclaturale
TAXREF v18 — INPN/MNHNSynonymes (3)— redirigent vers cette page
- Eupleres goudotii goudotiiDoyère, 1835
- Eupleres goudotii majorLavauden, 1929
- Eupleres majorLavauden, 1929
Sources : Catalogue of Life Cross-References (synonymes) · TAXREF v18 INPN/MNHN (commentaires FR).