
Chat tigre du sud
Leopardus guttulus(Hensel, 1872)
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Pays · région · aire protégée · écorégion · biome
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Calcul du tissu écologique de Leopardus guttulus.
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Liste rouge IUCN
VU · Vulnérablecritères C1↘Décroissante- Évaluation
- 2016 · v3.1
- Altitude
- 0 – 2000 m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
Leopardus guttulus population densities vary, but tend to be low throughout most of its range especially in regard to what would be expected of such a small cat species. Given its body size, expected density would be 91/100 km². Population densities of L. guttulus vary from one to 25/100 km². It is generally around 1-5/100 km² (or even lower) in most of its area of occupancy but can get to 13-25/100 km² in a few isolated high density areas (Oliveira 2011, Oliveira et al. 2013). Higher densities are attained only where Ocelots are absent or very rare. Where Ocelots are common or attain densities of 10/100 km² or higher, the Southern Tiger Cat is extremely rare and is expected to reach numbers much lower than 1-5/100 km². Thus, the Southern Tiger Cat is negatively impacted by Ocelots by interspecific killing due to potential for competition in what is known as the “Ocelot effect” (Oliveira et al. 2010, Oliveira 2011).
The state of Santa Catarina in southern Brazil has been considered the most important area for Leopardus guttulus conservation and thus to harbour the best and likely most viable population. This is due to the extent of the state’s remaining Atlantic Forest, level of connectivity and the cat’s presence in reasonable numbers in local Conservation Units due in most part to the absence of Ocelots (Oliveira et al. 2008). Nevertheless, previous high densities found in some areas there (25/100 km²) seemed to have dropped to 13/100 km² or 7/100 km² in the past few years, likely as a consequence of natural rodent reduction (Oliveira et al. 2013, M. Tortato pers. comm.). Therefore, expected higher densities of this species might be lower than previously thought. Considering all remaining area of natural habitat there and the species densities recorded, population size in Santa Catarina is expected to be around 1,500–2,800 (more likely towards the lower limit). Elsewhere, population reductions of ca. 67% have been observed due to an increase in number of Ocelots (Oliveira 2011, Marques 2013). At other areas, reductions from 20-24/100 km2 to 8/100km2 have also been noted (Oliveira 2011, Kasper et al. 2015), but not as a consequence of the Ocelot effect.
Likely as a consequence of the Ocelot effect, L. guttulus is found mostly outside protected areas of two of South America’s most threatened biomes, the highly fragmented Atlantic Forest, whose natural cover remaining is around 8% and the savannahs, whose remaining area is <40%. In this way, conservation efforts should focus outside protected areas.
A declining global population of about 6,047 mature individuals of L. guttulus was estimated, given its expected maximum area of occupancy (AOO) and typical lower population densities (Oliveira 2011; Oliveira et al. 2010, 2013). Given the likely overestimation of the AOO, using the lower known density estimate values is warranted to compensate and avoid an unrealistic population overestimation. A future decline of 10–30% over the next 15-18 years (= three generations) is projected due to declining AOO (habitat loss) and habitat quality. Even though the Southern Tiger Cat is found in several protected areas, no conservation units within the species’ range in Brazil or elsewhere are expected to house 500 individuals, most far below 200 (Oliveira et al. 2008).
The state of Santa Catarina in southern Brazil has been considered the most important area for Leopardus guttulus conservation and thus to harbour the best and likely most viable population. This is due to the extent of the state’s remaining Atlantic Forest, level of connectivity and the cat’s presence in reasonable numbers in local Conservation Units due in most part to the absence of Ocelots (Oliveira et al. 2008). Nevertheless, previous high densities found in some areas there (25/100 km²) seemed to have dropped to 13/100 km² or 7/100 km² in the past few years, likely as a consequence of natural rodent reduction (Oliveira et al. 2013, M. Tortato pers. comm.). Therefore, expected higher densities of this species might be lower than previously thought. Considering all remaining area of natural habitat there and the species densities recorded, population size in Santa Catarina is expected to be around 1,500–2,800 (more likely towards the lower limit). Elsewhere, population reductions of ca. 67% have been observed due to an increase in number of Ocelots (Oliveira 2011, Marques 2013). At other areas, reductions from 20-24/100 km2 to 8/100km2 have also been noted (Oliveira 2011, Kasper et al. 2015), but not as a consequence of the Ocelot effect.
Likely as a consequence of the Ocelot effect, L. guttulus is found mostly outside protected areas of two of South America’s most threatened biomes, the highly fragmented Atlantic Forest, whose natural cover remaining is around 8% and the savannahs, whose remaining area is <40%. In this way, conservation efforts should focus outside protected areas.
A declining global population of about 6,047 mature individuals of L. guttulus was estimated, given its expected maximum area of occupancy (AOO) and typical lower population densities (Oliveira 2011; Oliveira et al. 2010, 2013). Given the likely overestimation of the AOO, using the lower known density estimate values is warranted to compensate and avoid an unrealistic population overestimation. A future decline of 10–30% over the next 15-18 years (= three generations) is projected due to declining AOO (habitat loss) and habitat quality. Even though the Southern Tiger Cat is found in several protected areas, no conservation units within the species’ range in Brazil or elsewhere are expected to house 500 individuals, most far below 200 (Oliveira et al. 2008).
Menaces identifiées(12 menaces classées CMP-IUCN)
1_1Housing & urban areasRapid DeclinesMajority (50-90%)Ongoing1_2Commercial & industrial areasRapid DeclinesMajority (50-90%)Ongoing2_3_3Agro-industry grazing, ranching or farmingRapid DeclinesMajority (50-90%)Ongoing5_1_3Persecution/controlCausing/Could cause fluctuationsMinority (<50%)Ongoing7_1_1Increase in fire frequency/intensityCausing/Could cause fluctuationsMinority (<50%)Ongoing8_1_1Unspecified speciesCausing/Could cause fluctuationsMajority (50-90%)Ongoing2_2_2Agro-industry plantationsVery Rapid DeclinesMajority (50-90%)Ongoing4_1Roads & railroadsMinority (<50%)Ongoing7_3Other ecosystem modificationsOngoing8_3Introduced genetic materialUnknownOngoing
+ 2 menaces supplémentaires
Description complète des menacesTexte détaillé évaluation IUCNExpert
The Southern Tiger Cat was heavily exploited for the fur trade decades ago, following the decline in Ocelot trade. Although international trade ceased, there is still some localized illegal hunting, usually for the domestic market. A population decline in the past few years has been detected in Santa Catarina state in Brazil, the area considered the most important for its conservation, where the density estimates dropped by more than 50%, probably as a consequence of prey reduction (Oliveira et al. 2008, 2013; M.A. Tortato pers. comm.). Additionally, the existing global population is still suffering from habitat loss and fragmentation, which in the case of the Cerrado biome is undergoing high rates of loss (Klink and Machado 2005, MMA/IBAMA 2011). Other threats include hunting due to conflicts with rural owners, competition and diseases spread by domestic dogs, indiscriminate use of rodent poisoning, and road kills (Oliveira et al. 2008, 2013; Baréa and Leite 2012; R. Leite-Pitman and T. Trigo pers. comms.). It is also very important to consider the existence of an extensive hybridization zone between L. guttulus and Leopardus geoffroyi on the geographic limits of their distribution that may be affecting the genetic uniqueness of this species, as 38.2% of the Southern Tiger Cat specimens there are introgressed from the latter (Trigo et al. 2008, Trigo et al. 2013a).
Habitats préférentiels (classification IUCN)
1_5Forest - Subtropical/Tropical Dry★1_6Forest - Subtropical/Tropical Moist Lowland★1_9Forest - Subtropical/Tropical Moist Montane★2_1Savanna - Dry★1_7Forest - Subtropical/Tropical Mangrove Vegetation Above High Tide Level1_8Forest - Subtropical/Tropical Swamp
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
Leopardus guttulus is not formally included on CITES Appendix I as a separate species yet (but would be automatically included as L. tigrinus). Prior to its separation from L. tigrinus, its commercial use was legally forbidden. Technically, as all Felidae not listed on Appendix I are in Appendix II, it would automatically be under Appendix II. Hunting of the species is prohibited in Argentina, Brazil, and Paraguay (Nowell and Jackson 1996). This species is Vulnerable in Argentina – still under L. tigrinus (Diaz and Ojeda 2000) and Brazil (MMA 2014). Populations in protected areas are expected to be very low, probably because of the impact of the higher Ocelot densities and, as such, conservation efforts will have to focus outside protected areas (Oliveira et al. 2008, Oliveira 2011). These areas are, in turn, under intense pressure from impacts, either of fragmentation and/or area loss. Further studies are required on the species' ecology, demographics, natural history, and threats.
Actions de conservation (5)Conservation Actions Classification Scheme — IUCNExpert
1_1Site/area protection1_2Resource & habitat protection2_2Invasive/problematic species control2_3Habitat & natural process restoration5_2Policies and regulations
Stress écologiques (16)Stresses Classification — IUCNExpert
1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation2_1Species mortality2_1Species mortality2_1Species mortality2_1Species mortality2_3_1Hybridisation2_3_1Hybridisation
Priorités de recherche (7)Research Needed Classification — IUCNExpert
1_1Taxonomy1_2Population size, distribution & trends1_3Life history & ecology1_5Threats2_1Species Action/Recovery Plan3_1Population trends3_4Habitat trends
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Neotropical
Systèmes (terrestre/eau douce/marin)
Terrestrial
Références bibliographiques (23)Sources scientifiques de l'évaluation IUCNExpert
- Kasper, C.B., Schneider, A. and Oliveira T.G. de. 2016. Home range and density of three sympatric felids in the southern Atlantic Forest, Brazil. <i>Brazilian Journal of Biology </i> 76: 228-232.
- IUCN. 2016. The IUCN Red List of Threatened Species. Version 2016-2. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 04 September 2016).
- Ministério do Meio Ambiente - MMA. 2014. Portaria 444 - Lista Nacional Oficial de Espécies de Fauna Ameaçadas de Extinção. DOU 245.
- Trigo, T.C., Tirelli, F.P., Machado, L.F., Peters, F.B., Indrusiak, C.B., Mazim, F.D., Sana, D., Eizirik, E. and Freitas, T.R.O. 2013b. Geographic distribution and food habits of <i> Leopardus tigrinus </i> and <i> L. geoffroyi</i> (Carnivora, Felidae) at their geographic contact zone in southern Brazil. <i>Studies on Neotropical Fauna and Environment</i> 48: 56-67.
- Trigo, T.C., Schneider, A., de Oliveira,T.G., Lehugeur, L.M., Silveira, L., Freitas, T.R.O. and Eizirik, E. 2013a. Molecular data reveal complex hybridization and a cryptic species of Neotropical wild cat. <i>Current Biology</i> 23(24): 2528–2533.
- Oliveira, T.G. de, Tortato, M.A, Almeida, L. B. de, Campos, C.B. and Beisiegel, B.M. 2013. Avaliação do risco de extinção do gato-do-mato <i>Leopardus tigrinus</i> no Brasil. <i>Biodiversidade Brasileira</i> 31: 56-65.
- Marques, R.V. 2013. Riqueza de espécies, frequência relativa, padrão de atividades de mamíferos de médio e grande porte e abundância de felinos em floresta ombrófila mista. PhD dissertation, Universidade Federal do Rio Grande do Sul.
- Baréa, C.F.S. and Leite, M.R.P. 2012. Diagnosticando a presença do gato-do-mato (<i>Leopardus tigrinus</i>) em diversos ambientes do Parque Estadual Serra da Baitaca e seu entorno. Quatro Barras, PR. Report., PUC-Paraná.
- Oliveira, T.G. de. 2011. Ecologia e conservação de pequenos felinos no Brasil e suas implicações para o manejo. PhD dissertation, Universidade Federal de Minas Gerais.
- Ministério do Meio Ambiente - MMA / Instituto Brasileiro de Meio Ambiente e Recursos Naturais Renováveis – IBAMA. 2011. Monitoramento do bioma Cerrado 2008-2009. MMA, Brasília, DF, Brazil.
- Nascimento, F. O. d. 2010. Revisão taxonômica do gênero Leopardus Gray, 1842 (Carnivora, Felidae). Universidade de São Paulo.
- Oliveira, T.G. de, Tortato, M.A., Silveira, L., Kasper, C.B., Mazim, F.D., Lucherini, M. Jácomo, A.T., Soares, J.B.G., Marques, R.V. and Sunquist, M. 2010. Ocelot ecology and its effect in the small-felid guild in the lowland Neotropics. In: D.W. Macdonald and A. Loveridge (eds), <i>Biology and Conservation of Wild Felids</i>, pp. 563-584. Oxford University Press, Oxford.
- Tortato, M.A. 2009. Disponibilidade e uso de presas na dieta do gato-do-mato-pequeno, <i> Leopardus tigrinus</i> (Schreber, 1775) em área de restinga no sul do Brasil. MSc Thesis, Universidade Federal do Paraná.
- Trigo, T.C., Freitas, T.R.O., Kunzler, G., Cardoso, L., Silva, J.C.R., Johnson, W.E., O’Brien, S.J., Bonatto, S.L. and Eizirik, E. 2008. Inter-species hybridization among Neotropical cats of the genus <i>Leopardus</i>, and evidence for an introgressive hybrid zone between <i>L. geoffroyi</i> and <i>L. tigrinus</i> in southern Brazil. <i>Molecular Ecology</i> 17: 4317-4333.
- Oliveira, T.G. de, Kasper, C.B., Tortato, M.A., Marques, R.V., Mazim, F.D. and Soares, J.B.G. 2008. Aspectos ecológicos de <i>Leopardus tigrinus</i> e outros felinos de pequeno-médio porte no Brasil. In: T.G. de Oliveira (ed.), <i>Plano de ação para conservação de Leopardus tigrinus no Brasil</i>, Instituto Pró-Carnívoros/Fundo Nacional do Meio Ambiente, Atibaia, SP, Brazil.
- Klink, C.A. and Machado, R.B. 2005. Conservation of the Brazilian Cerrado. <i>Conservation Biology</i> 19(3): 707-713.
- Tortato, M.A. and Oliveira, T.G. de. 2005. Ecology of the oncilla (<i>Leopardus tigrinus</i>) at Serra do Tabuleiro State Park, Southern Brazil. <i>Cat News</i> 42: 28-30.
- Oliveira, T.G. de and Cassaro, K. 2005. Guia de campo dos felinos do Brasil. Instituto Pró - Carnívoros/Fundação Parque Zoológico de São Paulo/Sociedade de Zoológicos do Brasil/Pró, Vida Brasil, São Paulo.
- Facure-Giaretta, K.G. 2002. Ecologia alimentar de duas espécie s de felinos do gênero <i>Leopardus</i> em uma floresta secundária no sudeste do Brasil. PhD dissertation, Universidade Estadual de Campinas.
- Diaz, G.B. and Ojeda, R.A. 2000. <i>Libro rojo de los mamíferos de Argentina</i>. SAREM, Buenos Aires.
- Johnson, W.E., Slattery, J.P., Eizirik, E., Kim, J.H., Raymond, M.M., Bonacic, C., Cambre, R., Crawshaw, P., Nunes, A., Seuanez, H.N., Moreira, M.A.M., Seymour, K.L., Simon, F., Swanson, W. and O'Brien, S.J. 1999. Disparate phylogeographic patterns of molecular genetic variation in four closely related South American small cat species. <i>Molecular Ecology</i> 8: S79-S94.
- Nowell, K. and Jackson, P. (compilers and editors). 1996. Wild Cats. Status Survey and Conservation Action Plan. IUCN/SSC Cat Specialist Group. IUCN, Gland, Switzerland.
- Hensel, R. 1872. <i>Beiträge zur Kenntniss der Säugethiere Süd-Brasiliens</i>. Buchdrukerei der Königlichen Akademie der Wissenschaften, Berlin.
Évaluateurs & contributeurs (2)Personnes ayant contribué à l'évaluation IUCNExpert
assessor
de Oliveira, T., Trigo, T., Tortato, M., Paviolo, A., Bianchi, R. & Leite-Pitman, M.R.P.
evaluator
Nowell, K., Hunter, L., Schipper, J., Breitenmoser-Wursten, C., Lanz, T. and Breitenmoser, U.
de Oliveira, T., Trigo, T., Tortato, M., Paviolo, A., Bianchi, R. & Leite-Pitman, M.R.P. 2016. Leopardus guttulus. The IUCN Red List of Threatened Species 2016: e.T54010476A54010576. Accessed on 05 May 2026.
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
Note nomenclaturale & synonymesDétails taxonomiques + synonymes CoLExpert
Note nomenclaturale
TAXREF v18 — INPN/MNHNSynonymes (2)— redirigent vers cette page
- Felis guttulaHensel, 1872
- Leopardus tigrinus guttulus(Hensel, 1872)
Sources : Catalogue of Life Cross-References (synonymes) · TAXREF v18 INPN/MNHN (commentaires FR).