Ontologia
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Lycalopex vetulus(Lund, 1842)

NTLR Monde (IUCN)
  1. Animal
  2. Chordata
  3. Mammalia
  4. Carnivora
  5. Canidae
1 photo · Licences CC (Wikimedia Commons / iNaturalist)Click pour agrandir

Description

espèce de mammifères

Source : Wikidata

Pays · région · aire protégée · écorégion · biome

Graphe en cours d’indexation

Calcul du tissu écologique de Lycalopex vetulus.

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Liste rouge IUCN

NT · Quasi menacéecritères C1Décroissante
Évaluation complète
Évaluation
2020 · v3.1
Altitude
901100 m
Profondeur
m
État de la populationExpert
Only two studies have previously estimated population densities of the Hoary Fox. Rocha et al. (2008) used linear transects at two locations in Mato Grosso and estimated 1.21 individuals per km² in an area covered by shrub savannah and 4.28 individuals per km² in an exotic grass pasture. However, these estimates should be cautiously interpreted since it is possible that the difference in density is biased by: i) the species' detectability in the different environments, and ii) the timing of sampling in different reproductive seasons. The 4.28 density was estimated in the second semester, when foxes are known to be denning and foraging with puppies together, and this may have overestimated density at the pasture site. Rezende (2018), using capture-recapture models accounting for imperfect detectability, estimated 0.41 individual per km2 in a fragmented area comprising a matrix of exotic pastures in south-eastern Goiás. In the same region/population, Lemos and Azevedo (unpublished data) registered offspring mortality greater than 50% in cohorts monitored during 12 years, with potentially negative demographic impacts.

To estimate the population size of the Hoary Fox, the total area of suitable habitat was determined taking into account remnants of Cerrado habitats (grassland, savannah, and other non-forest), and 50% of the area of pastures, within the species’ current range, yielding an area of approximately 120,000 km². Considering the limited information on density for the species in disturbed and natural habitats (0.41 individual per km², Rezende 2018; 1.21 individuals per km², Rocha et al. 2008), the habitats known to be used and the anthropogenic threats across most of the range, it was estimated that the Hoary Fox population might be approximately 49,200-96,000 individuals (based on a mean density of 0.8 individual per km²). Number of mature individuals may vary according to species life stories, degree of habitat specificity, mortality rates, and how isolated subpopulations are. There are no available data on the number of mature individuals among different Hoary fox subpopulations. From a monitored subpopulation of Cumari, south-eastern Goiás, not all adults were able to find a mate and breed annually, and mortality of adults and dispersing young was high. Breeding males and females represented about 20-25% of monitored individuals annually (Lemos and Azevedo, pers. obs). On the other hand, genetic data obtained from Cumari and a second subpopulation from Araguari, western Minas Gerais, suggest high genetic diversity of individuals (He = 0.816, Silva 2015), despite the high degree of human disturbance in sampled areas. On a wider phylogeographic perspective, Garcez (2019) also infers that the population of Hoary Foxes is structured in only one population along Brazil, not showing signs of isolation or fragmentation. Therefore, considering 20-25% of the population is capable of reproducing, the high mortality rates of adults and dispersing young, and the low densities registered, the number of mature individuals is estimated to range between 9,840 and 19,200 mature individuals.

Considering the joint impacts of ongoing loss of habitat, road-kills, persecution, killing and transmission of diseases by domestic dogs, retaliation for the alleged predation of domestic fowl, high mortality of pups/juveniles in different populations along unprotected areas, and that this is common throughout the species distribution, it is not unreasonable to estimate that in 12 years (three generations) a decline of at least 10% of the population could occur.

Menaces identifiées(4 menaces classées CMP-IUCN)

  • 5_1_3
    Persecution/control
    UnknownMinority (<50%)Ongoing
  • 2_1_3
    Agro-industry farming
    Slow, Significant DeclinesMajority (50-90%)Ongoing
  • 2_3_3
    Agro-industry grazing, ranching or farming
    Slow, Significant DeclinesMajority (50-90%)Ongoing
  • 4_1
    Roads & railroads
    Slow, Significant DeclinesMajority (50-90%)Ongoing
Description complète des menacesExpert
The major threats to the Hoary Fox are habitat destruction and other direct and indirect anthropogenic effects (Lemos, Azevedo et al. 2011, Lemos et al. 2013, Lemos 2016). The species is endemic to the Cerrado, which was historically seen as unproductive land. However, extensive commercial and industrial development in the region over the last two decades, characterized by growth (in size and number) of urban centres, increased timber exploitation for coal provision, conversion of natural habitats to pastures and crops, and the expansion of linear structures for transportation of rural products has resulted in loss and fragmentation of the original Cerrado habitats (Dalponte 2003, Lemos and Azevedo 2009, Lemos, Azevedo et al. 2011, Lemos et al. 2013). Natural Cerrado areas in São Paulo and Minas Gerais occur in small and scattered fragments, and are currently isolated from the northern, more continuous portion of the biome.

Road kills are responsible for a high number of individuals being lost from populations (Dalponte 2003, Dalponte and Courtenay 2004, Lemos and Azevedo, 2009, Lemos, Azevedo et al. 2011, Lemos 2016), followed by attacks by domestic dogs and human persecution in response to an erroneous perception that Hoary Foxes attack domestic fowl (Dalponte 2003, Lemos and Azevedo 2009, Lemos, Azevedo et al. 2011, Lemos et al. 2013, Bickley et al. in press). In fact, domestic fowl are mostly absent from the Hoary Fox diet (Lemos, Facure et al. 2011, Kotviski et al. in press). During population monitoring (n = 40 individuals) in Cumari, south-eastern Goiás, 29 Hoary Fox carcasses were retrieved, with the cause of mortality identified as: road-kills (n = 5), attacks by domestic dogs (n = 1), poisoning/gunshot (n = 3), predation by cougars (n = 7) and old age (n = 1). Mortality causes for 12 individuals were impossible to determine, but it is possible that diseases may have played a role.

Increasing contact between Hoary Foxes and humans and domestic animals may be leading to the development of novel eco-epidemiologic relationships as observed in Cumari (Goiás state). Hoary Foxes are frequently observed foraging among cattle and in close contact with human residences, and involved in antagonistic encounters with domestic dogs (Lemos, Azevedo et al. 2011). An infection of canine distemper virus (CDV) has been reported in a wild Hoary Fox and the potential sources of infection were domestic dogs (Megid et al. 2010). This report highlights the susceptibility of the species to CDV, with clinical and hystopathological signs identical to those developed by domestic dogs. There are also reports of two individuals that tested positive for canine parvovirus (Curi 2005). In the past, Hoary Foxes were identified as reservoirs of Leishmania chagasi (Deane and Deane 1954). However, Courtenay et al. (1996) compared craniums and demonstrated that infected individuals were in fact misidentified Crab-eating Foxes. There are no reports of rabies for the species. Hoary Foxes of two populations sampled in Cumari (Goiás) and Araguari (Minas Gerais) showed positive seroprevalence for Trypanosoma cruzi (71%) and Leptospira spp. (14.2%). However, parasites were not isolated, and there were no parasitemia cases nor clinical signs. Therefore, clinical and epidemiological importance of these parasites for Hoary Foxes is still unclear (Rocha et al. 2013, Rodrigues et al. 2015). Consequently, long-term studies to elucidate the susceptibility of this species to pathogens and understand the effects of these parasites on the survival of populations in natural and human-modified areas across its range are urgently needed.

Habitats préférentiels (classification IUCN)

  • 2_1Savanna - Dry
  • 14_2Artificial/Terrestrial - Pastureland
  • 14_1Artificial/Terrestrial - Arable Land
Mesures de conservation recommandéesExpert
Legislation
Not included on the CITES Appendices. Hunting and trade in wildlife is forbidden in Brazil. There is no specific hunting legislation for Hoary Foxes. 

Presence in protected areas
The species occurs in a number of protected areas throughout its range, including Águas Emendadas Ecological Station (ES), Santa Bárbara ES, Jataí ES, Ribeirão Preto ES, Serra das Araras ES, Chapada dos Veadeiros National Park (NP), Emas NP, Brasília NP, Grande Sertão Veredas NP, Serra da Canastra NP, Serra do Cipó NP, Chapada dos Guimarães NP, Serra da Capivara NP, Rio da Casca State Ecological Station (SES), Rio Ronuro SES, Serra de Caldas Novas State Park (SP), Pau Furado SP, Mirador SP, Serra Azul SP, Gruta da Lagoa Azul SP, Cajuru State Forest (SF), Batatais SF, Bebedouro SF,  Limoeiro Environmental Protection Area (EPA), Chapada dos Guimarães EPA, Bacaba Municipal Ecological Station (MES), Serra do Tombador Private Reserve of Natural Heritage (PNHR) (Cabral et al. 2017), Panga PNHR (Bruna et al. 2010), Galheiro PNHR, Santo Antonio Natural Monument (NM), and Cabeceira do Rio Coxipozinho Municipal Natural Park (MNP).

Presence in captivity
Although known to occur in captivity, no specimens were confirmed in Brazilian zoos and other wildlife keeping facilities at the time of assessing the species. 

Gaps in Knowledge
Areas for further research include: i) population studies in protected areas in order to establish base-line  information of Hoary foxes, ii) population dynamics in regions under different degrees of conservation and land use, and the real impact of human activities on populations occurring on private lands; iii) estimates of birth and death rates, longevity, and dispersal potential of juveniles; iv) investigation into the genetic viability of different subpopulations and the effects of hybridization with Pampas Foxes at São Paulo state; and v) an evaluation of the potential role of disease in population dynamics and the status of the Hoary Fox as potential reservoir of veterinary (e.g., scabies, CDV) and public health (e.g., leishmaniasis, rabies) pathogens.

Priorities for action
In 2013 an evaluation of the extinction risk for the Hoary Fox was conducted and the species was considered Vulnerable by the Brazilian Red List of Species Threatened of Extinction (Lemos et al. 2013). Based on this assessment, the species was included in the National Plan for the Conservation of Brazilian Canids published in 2018 by the National Center for Research and Conservation of Mammalian Carnivores/Chico Mendes Institute for Biodiversity Conservation (CENAP/ICMBio). The document contains specific actions for the conservation of Brazilian canids threatened with extinction to be held between 2018 and 2022, planed in association with governmental institutions, researchers and the private sector. Proposed actions include prioritizing the protection of Cerrado-specific habitats adequate for the survival of the species. Government and private projects and initiatives that aim at reducing negative impacts on the Cerrado, in addition to actions from rural development policies targeting sustainable production and development, and biodiversity maintenance in agro-ecosystems (Dalponte 2003), can effectively contribute to the conservation of the Hoary Fox in human-modified landscapes.
Actions de conservation (2)Expert
  • 2_1Site/area management
  • 4_3Awareness & communications
Stress écologiques (7)Expert
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 2_1Species mortality
  • 2_1Species mortality
Priorités de recherche (3)Expert
  • 1_2Population size, distribution & trends
  • 1_3Life history & ecology
  • 1_5Threats
Niche IUCN globaleExpert

Royaumes biogéographiques

Neotropical

Systèmes (terrestre/eau douce/marin)

Terrestrial
Références bibliographiques (30)Expert
  1. Bickley, S.M., Lemos, F.G., Gilmore, M.P., Azevedo, F.C., Freeman, E.W. and Songsasen, N. in press. Human perceptions and interactions with wild canids on cattle ranches in Central Brazil. <i>Oryx</i>.
  2. Kotvisky, B.M., Giaretta, K.G.F., Azevedo, F.C., Freitas-Junior, M.C. and Lemos, F.G. in press. Trophic niche overlap and resource partitioning among wild canids in an anthropized Neotropical ecotone. <i>Mastozoologia Neotropical</i>.
  3. IUCN. 2020. The IUCN Red List of Threatened Species. Version 2020-2. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 13 June 2020).
  4. Garcez, F.S. 2019. 2019. Inferências acerca de uma recém-descoberta zona híbrida entre duas espécies do gênero Lycalopex (Carnivora, Canidae), utilizando uma abordagem genômica. Tese de Doutorado em Ecologia e Evolução da Biodiversidade, Pontifícia Universidade Católica do Rio Grande do Sul.
  5. Dalponte, J.C., Lima, H.S., Klorfine, S. and Luz, N.C. 2018. Home range and spatial organization by the hoary fox <i>Lycalopex vetulus</i> (Mammalia: Carnivora: Canidae): response to social disruption of two neighboring pairs. <i>Journal of Threatened Taxa</i> 10(6): 11703–11709.
  6. Dalponte, J.C., Oliveira, J.S. and Lacerda, A.C.R. 2018. Occurrence of <i>Lycalopex vetulus</i> (Carnivora, Canidae) in the Cerrado-Amazon forest ecotone and Pantanal. <i>Acta Zoológica Platense</i> 18: 1–10.
  7. Rezende, L.R. 2018. Densidade e tamanho populacional de raposas-do-campo <i>Lycalopex vetulus</i> em um agroecossistema no Brasil Central. Trabalho de Conclusão de Curso (Graduação em Ciências Biológicas), Universidade Federal de Goiás.
  8. Cabral, R., Zanin, M., Porfírio, G. and Brito, D. 2017. Medium-sized to large mammals of Serra do Tombador, Cerrado of Brazil. <i>Checklist</i> 13: 1–6.
  9. Lemos, F.G. 2016. Ecologia e conservação da raposa-do-campo (<i>Lycalopex vetulus</i>) e suas interações com canídeos simpátricos em áreas antropizadas de Cerrado do Brasil Central. Tese de Doutorado em Ecologia e Conservação de Recursos Naturais, UFU. Uberlândia-MG.
  10. Rodrigues, T.C.S., Santos, A.L.Q., Lima-Ribeiro, A.M.C., Lemos, F.G., Azevedo, F.C., Arrais, R.C., Gomes, D.O. and Tavares, T.C.F. 2015. Occurrence of antibodies against <i>Leptospira</i> spp. in free-ranging wild canids from the Brazilian savanna. <i>Pesquisa Veterinária Brasileira</i> 35: 734-740.
  11. Silva, A.P. 2015. Análise da variabilidade genética e parentesco de <i>Lycalopex vetulus</i> (LUND, 1842), de uma região de cerrado do norte de Minas Gerais e sudeste de Goiás – Brasil. Dissertação de Mestrado em Ecologia e Recursos Naturais da Universidade Federal de São Carlos.
  12. Rocha, F.L, Roque, A.L.R., Lima, J.S., Cheida, C.C., Lemos, F.G., Azevedo, F.C., Arrais, R.C., Bilac, D., Herrera, H.M., Mourão, G. and Jansen, A.M. 2013. <i>Trypanosoma cruzi</i> Infection in Neotropical Wild Carnivores (Mammalia: Carnivora): At the Top of the <i>T. cruzi</i> Transmission Chain. <i>PLoS ONE</i> 8(7): e67463.
  13. Lemos, F.G., Azevedo, F.C., Beisiegel, B.M., Jorge, R.P.S., Paula, R.C., Rodrigues, F.H.G. and Rodrigues, L.A. 2013. Avaliação do risco de extinção da raposa-do-campo <i>Lycalopex vetulus</i> (Lund, 1842) no Brasil. <i>Biodiversidade Brasileira</i> 3(1): 160-171.
  14. Olifiers, N. and Delciellos, A.C. 2013. New record of <i>Lycalopex vetulus</i> (Carnivora, Canidae) in Northeastern Brazil. <i>Oecologia Australis</i> 17(4): 533-537.
  15. Austin, J.J., Soubrier, J., Prevosti, F.J., Prates, L., Trejo, V., Mena, F. and Cooper, A. 2013. The origins of the enigmatic Falkland Islands wolf. <i>Nature Communications</i> 4: 1552.
  16. Fernandes, F.A.B. and Costa, M.D. 2013. Mammalia, Carnivora, Canidae, <i>Pseudalopex vetulus</i> (Lund, 1842): First record for the Atlantic Forest, southern state of Minas Gerais, Brazil. <i>CheckList</i> 9(6): 1603-1604.
  17. Lemos, F.G., Azevedo, F.C., Costa, H.C.M. and May Junior, J.A. 2011. Human threats to hoary and crab-eating foxes in central Brazil. <i>Canid News</i> 14(2): 1-6.
  18. Lemos, F.G. and Facure, K.G. 2011. Seasonal variation in foraging group size of crab-eating foxes and hoary foxes in the Cerrado biome, Central Brazil. <i>Mastozoología Neotropical</i> 18: 239-245.
  19. Lemos, F.G., Facure, K.G. and Azevedo, F.C. 2011. Comparative ecology of the hoary fox and the crab-eating fox in a fragmented landscape in the Cerrado biome at Central Brazil. In: Rosalino, L.M. and Gheler-Costa, C. (eds), <i>Middle-sized carnivores in agricultural landscapes</i>, pp. 143-160. Nova Science Publishers, Inc, New York.
  20. Bruna, E.M., Guimarães, J.F., Lopes, C.T., Duarte, P., Gomes, A.N.L., Belentani, S.C.S, Pacheco, R., Facure, K.G., Lemos, F.G. and Vasconcelos, H.L. 2010. Mammalia, Estação Ecológica do Panga, a cerrado protected area in Minas Gerais State, Brazil. <i>Checklist</i> 6: 668-675.
  21. Perini, F.A., Russo, C.A.M. and Schrago, C.G. 2010. The evolution of South American endemic canids: a history of rapid diversification and morphological parallelism. <i>Journal of Evolutionary Biology</i> 23: 311-322.
  22. Megid, J., Teixeira, C.R., Amorin, R.L., Cortez, A., Heinemann, M.B., Antunes, J.M.A. de P., da Costa, L.F., Fornazari,F., Cipriano, J.R.B., Cremasco, A. and Richtzenhain, L.J. 2010. First identification of canine distemper virus in hoary fox (<i>Lycalopex vetulus</i>): pathologic aspects and virus phylogeny. <i>Journal of Wildlife Diseases</i> 46: 303-305.
  23. MMA/IBAMA/PNUD (Cooperação técnica). 2009. Relatório técnico de monitoramento do desmatamento no Bioma Cerrado, 2002 a 2008: Dados Revisados.
  24. Lemos, F.G. and Azevedo, F.C. 2009. <i>Lycalopex vetulus</i> (Lund, 1842). In: Bressan, P.M., Kierulff, M.C.M. and Sugieda, A.M. (eds), <i>Fauna ameaçada de extinção no Estado de São Paulo – vertebrados</i>, pp. 61. Fundação Parque Zoológico de São Paulo / Secretaria do Meio Ambiente, São Paulo.
  25. Slater, G.J., Thalmann, O., Leonard, J., Schweizer, R.M., Koepfli, K-P., Pollinger, J.P., Rawlence, N.J., Austin, J.J., Cooper, A. and Wayne, R.K. 2009. Evolutionary history of the Falklands wolf. <i>Current Biology</i> 19: 937–938.
  26. Dalponte, J. C. 2009. <i>Lycalopex vetulus</i> (Carnivora: Canidae). <i>Mammalian Species</i> 847: 1-7.
  27. Rocha, E.C., Silva, E., Feio, R.N., Martins, S.V. and Lessa, G. 2008. Densidade populacional de raposa-do-campo <i>Lycalopex vetulus</i> (Carnivora, Canidae) em áreas de pastagem e campo sujo, Campinápolis, Mato Grosso, Brasil. <i>Iheringia, Série Zoologia</i> 98: 78-83.
  28. Carnieli Jr., P., Fahl, W.O., Castilho, J.G., Oliveira, R.N., Macedo, C.I., Durymanova, E., Jorge, R.S.P., Morato, R.G., Spíndola, R.O., Machado, L.M., Carrieri, M.L. and Kotait, I. 2008. Characterization of rabies vírus isolated from canids and identification of the main wild canid host in Northeastern Brazil. <i>Virus Research</i> 131: 33-46.
  29. Lemos, F.G., Facure, K.G. and Da Costa, A.N. 2007. Interference competition between the crab-eating fox and the hoary fox. <i>Canid News</i> 10(3): 1-4.
  30. Courtenay, O., Macdonald, D.W., Gilingham, S., Almeida, G. and Dias, R. 2006. First observations on South America’s largely insectivorous canid: the hoary fox (<i>Pseudalopex vetulus</i>). <i>Journal of Zoology</i> 268: 45-54.
Évaluateurs & contributeurs (3)Expert
assessor
Lemos, F.G., Azevedo, F.C., Paula, R.C. & Dalponte, J.C.
evaluator
Hoffmann, M. & Sillero-Zubiri, C.
facilitators
Hoffmann, M.

Lemos, F.G., Azevedo, F.C., Paula, R.C. & Dalponte, J.C. 2020. Lycalopex vetulus. The IUCN Red List of Threatened Species 2020: e.T6926A87695615. Accessed on 05 May 2026.

Traits biologiques

20 valeurs · 5 sources

Morphologie(4)

Masse adulte
5,35 kg
AnAge
Longueur
-999 mm
PanTHERIA
Masse naissance
-999000 mg
PanTHERIA
Masse au sevrage
-999000 mg
PanTHERIA

Cycle de vie(1)

Longévité max
13 ans
AnAge
Voir 15 traits de plus (2 catégories)

Reproduction(6)

Maturité sexuelle
9,1 mois
AnAge
Gestation
1,8 mois
AnAge
Intervalle naissances
1 ans
AnAge
Taille de portée
3
AnAge
Portées par an
-999
PanTHERIA
Sevrage
-999 j
PanTHERIA

Écologie & habitat(9)

Fruits (%)
20 %
elton_mammals
Invertébrés (%)
10 %
elton_mammals
Nectar (%)
0 %
elton_mammals
Autre végétal (%)
10 %
elton_mammals
Charognard (%)
0 %
elton_mammals
Graines (%)
0 %
elton_mammals
Vert. ectothermes (%)
30 %
elton_mammals
Vert. endothermes (%)
30 %
elton_mammals
Poissons (%)
0 %
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 (3)— redirigent vers cette page

  • Canis vetulusLund, 1842
  • Dusicyon vetulusLund, 1842
  • Pseudalopex vetulus(Lund, 1842)

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