Ontologia
Chacal Commun

Chacal Commun

Canis aureusLinnaeus, 1758

LCLR Monde (IUCN)
  1. Animal
  2. Chordata
  3. Mammalia
  4. Carnivora
  5. Canidae
5 photos · 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 Canis aureus.

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

Liste rouge IUCN

LC · Préoccupation mineureCroissante
Évaluation complète
Évaluation
2025 · v3.1
Altitude
01800 m
Profondeur
m
État de la populationExpert
The Golden Jackal probably colonised Europe during the early Holocene (Spassov 1989, Sommer and Benecke 2005). Early remains were found in southern Greece and in Dalmatia in Croatia (Krofel et al. 2017). Golden Jackals remained limited to the small coastal areas of the Mediterranean and Black seas and their numbers were low until the 19th century, probably restricted by the presence of the Grey Wolf (Krofel et al. 2017). The first expansion into the Pannonian basin was detected in the 19th century. The expansion increased after World War II and has been very rapid since the 1970s, especially for the Pannonian-Balkan subpopulation. The estimated population size for Europe is between 97,000 and 117,000 Golden Jackals, of which approximately 84,000 are within the EU 27 (LCIE 2018). These are distributed in four subpopulations.

1. Pannonian-Balkan
According to an evaluation of the population in 2012-2016 (LCIE 2018), the subpopulation is estimated to be between 95,000 and 114,000 jackals and is increasing rapidly. The vast majority of the population is located in Bulgaria (46,000-61,000). Another five countries had high numbers of individuals: Serbia (c. 20,000), Hungary (c. 14,000), Romania (c. 10,000), Croatia (3,300-6,700) and Greece (c. 800). Numbers are also increasing in Bosnia and Herzegovina (300-500), Slovenia (150-350), Estonia (27 family groups in 2020; Männil and Ranc 2022) and North Macedonia (40-80). Few animals occur in Austria (minimum three family groups; Hatlauf et al. 2017). The population size of jackals in Slovakia is unknown but is growing (Urban et al. 2016, Guimarães et al. 2019). The first reproduction was recently detected in Czechia (Jirku et al. 2018), in Poland (Kowalczyk et al. 2020) and in Germany. The subpopulation is growing very rapidly as shown by temporal data. Relict populations in southeastern Bulgaria started to spread in the early 1960s. The distribution range increased 33-fold between 1962 and 1985, at accelerating rates (Kryštufek et al. 1997). In Serbia, the rapid expansion started at the beginning of the 1980s. Population estimates derived from hunting bag statistics suggest an exponential population growth (Ćirović et al. 2008, Heltai et al. 2013). Reproductive populations are now established throughout most of Serbia (Ćirović et al. 2008), where only vagrants are recorded. In Bosnia and Herzegovina, the population has been reported to be increasing since 2000 with an average 35% annual growth in hunting records. The highest densities are reported for the northern part of the country (Trbojević et al. 2018). In Hungary, the species went extinct in the middle of the 20th century, naturally recolonised in the 1990s, and is now expanding very rapidly (Heltai et al. 2000, Heltai et al. 2004). Golden Jackals were first noticed in Estonia and Latvia in 2011 and were thought to be the result of natural expansion (Rutkowski et al. 2015, Männil and Ranc 2022).

2. Adriatic
Throughout the 20th century, the subpopulation was gradually increasing and expanding towards the northwest from its historic stronghold, in southern Dalmatia, Croatia (Kryštufek and Tvrtković 1990). In 2016, the population was estimated to be 2,000-2,700 jackals and continues to increase (LCIE 2018). The vast majority of the population is located on the coast of Croatia (c. 1,300-1,600), mainly in Dalmatia (LCIE 2018). Golden Jackals are also present in Montenegro (400-700), mainland Greece (c. 120), southern Bosnia and Herzegovina (c.100) and western Slovenia (50-150). A few family groups occur in Italy (c. 3-9).

3. Peloponnese
The subpopulation in the Peloponnese declined between the 1980s and the early 2000s (Giannatos 2004, Giannatos et al. 2005). Since then, the subpopulation is increasing and there were an estimated 100-120 jackal family groups i.e., 400-480 individuals in 2015 (LCIE 2018).

4. Samos Island
The subpopulation of Golden Jackal on Samos Island is small, estimated in 2015 to be around 20 jackal family groups (i.e., around 80 individuals) and is thought to be stable (Giannatos et al. 2005, LCIE 2018). Golden Jackals most likely colonised Samos Island from nearby Türkiye (1.7 km away). Their presence was already reported during the 18th and 19th centuries (Masseti 2012). Their low genetic variability suggests that the subpopulation may be isolated from the mainland (Rutkowski et al. 2015).

Menaces identifiées(10 menaces classées CMP-IUCN)

  • 4_1
    Roads & railroads
    Causing/Could cause fluctuationsWhole (>90%)Ongoing
  • 5_1_2
    Unintentional effects (species is not the target)
    Causing/Could cause fluctuationsWhole (>90%)Ongoing
  • 5_1_3
    Persecution/control
    Causing/Could cause fluctuationsWhole (>90%)Ongoing
  • 1_1
    Housing & urban areas
    UnknownMinority (<50%)Ongoing
  • 1_3
    Tourism & recreation areas
    UnknownMinority (<50%)Ongoing
  • 2_1_1
    Shifting agriculture
    UnknownMajority (50-90%)Ongoing
  • 2_1_3
    Agro-industry farming
    UnknownMajority (50-90%)Ongoing
  • 6_1
    Recreational activities
    UnknownMinority (<50%)Ongoing
  • 7_1_1
    Increase in fire frequency/intensity
    UnknownMinority (<50%)Ongoing
  • 8_1_1
    Unspecified species
    UnknownMinority (<50%)Ongoing
Description complète des menacesExpert
Overall, the Golden Jackal appears to be a very successful species, which is increasingly expanding in Europe despite intensive persecution in several parts of the range. The Golden Jackal is often perceived negatively by the public despite the identified ecosystem services provided by the species (Ćirović et al. 2016), This negative opinion is mostly related to perceived conflicts with livestock owners and hunters (Mihelič and Krofel 2012), as well as from the perception of jackals as non-native animals due to recent colonisation of areas without historic presence (Trouwborst et al. 2015). Not surprisingly, the main threats to the species are related to legal culling, illegal killing and poisoning. In recent years some countries even aimed for complete eradication of the species (Trouwborst et al. 2015). Traffic accidents are also an important cause of mortality throughout the species range. Locally, changes in animal husbandry and waste management may reduce anthropogenic resource availability, on which jackals thrive, and this could reduce jackal survival and abundance (Kapota et al. 2016). Furthermore, agricultural intensification may reduce necessary cover in human-dominated landscapes (Giannatos 2004). Grey Wolves, especially when occurring in stable packs and ecologically effective densities, can reduce jackal abundance and range (Newsome et al. 2017), and local disappearances of territorial jackals have been recorded following wolf re-colonisation of some areas (Krofel et al. 2017). The potential impacts of diseases (rabies and sarcoptic mange, especially) and hybridisation with dogs remain to be studied, but may not be negligible (Galov et al. 2015). Although the aforementioned mortality factors tend to be ubiquitous throughout the species range, their relative importance may vary from subpopulation to subpopulation.

1. Pannonian-Balkan
The main threats to Golden Jackal in the Pannonian-Balkan subpopulation are, in order of importance, the low public acceptance related to real or perceived conflicts with livestock husbandry and hunters, traffic accidents, poisoning, intentional legal culling and illegal killing. Habitat modification and interference competition with Grey Wolves can locally be important as well as accidental illegal killing (e.g., non-targeted poisoning) and hybridisation with domestic dogs.

2. Adriatic

The main human threats to Golden Jackal in the Adriatic subpopulation are, in order of importance, the low public acceptance related to real or perceived conflicts with livestock husbandry and hunters, traffic accidents, intentional legal culling and illegal killing, as well as poisoning. Habitat modification and interference competition with Grey Wolves can locally be important as well as unintentional legal culling (e.g., erroneous killing during red fox hunting in Italy) and hybridisation with domestic dogs.

3. Peloponnese

The main human threats to Golden Jackal in the Peloponnese are, in order of importance, the decrease in anthropogenic resource availability (i.e., livestock carcasses, waste dumps), as well as the low public acceptance related to real or perceived conflicts with livestock husbandry. These are expected to intensify the changes in farming practices and traffic accidents, and to a minor extent, wildfires also impact the Golden Jackal subpopulation.

4. Samos Island

The main human threats to Golden Jackal in the Peloponnese are the decrease in anthropogenic resource availability (i.e., livestock carcasses, waste dumps) and traffic accidents. The low public acceptance related to real or perceived conflicts with livestock husbandry, and to a lesser extent, wildfires, also impact Golden Jackals on Samos Island.

Habitats préférentiels (classification IUCN)

  • 1_4Forest - Temperate
  • 3_4Shrubland - Temperate
  • 3_8Shrubland - Mediterranean-type Shrubby Vegetation
  • 4_4Grassland - Temperate
  • 5_4Wetlands (inland) - Bogs, Marshes, Swamps, Fens, Peatlands
  • 14_1Artificial/Terrestrial - Arable Land
  • 14_2Artificial/Terrestrial - Pastureland
  • 14_3Artificial/Terrestrial - Plantations
  • 14_5Artificial/Terrestrial - Urban Areas
Mesures de conservation recommandéesExpert
The Golden Jackal is listed in Annex V of the Habitats Directive, 92/43 EC as a species of community interest. The species’ status varies at the national level (see Trouwborst et al. 2015 for a full review, including a discussion of some of the management confusion due to recent range expansion and inadequate legal interpretation). The species (as a wider species concept that included African Wolf Canis lupaster) was previously assessed (Giannatos and Kryštufek 2007) in 2006 as Near Threatened for the EU 27 members states.

1. Pannonian-Balkan

Golden Jackals are fully protected in North Macedonia. They are hunted in Bosnia and Herzegovina, Bulgaria, Croatia, Hungary, Romania, Serbia, Slovakia, Slovenia and Ukraine. The species is unprotected in Estonia, Greece and Czechia. Its status is variable in Austria from region to region.

2. Adriatic

The species is fully protected in Albania and Italy. Golden Jackals are hunted in Bosnia and Herzegovina, Croatia, Montenegro and Slovenia. They are unprotected in Greece.

3. Peloponnese

The species is unprotected.

4. Samos Island

The species is unprotected.
Actions de conservation (3)Expert
  • 4_3Awareness & communications
  • 5_1_1International level
  • 5_1_2National level
Stress écologiques (19)Expert
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_2Species disturbance
  • 2_2Species disturbance
  • 2_2Species disturbance
  • 2_2Species disturbance
  • 2_2Species disturbance
  • 2_3_1Hybridisation
Priorités de recherche (8)Expert
  • 1_1Taxonomy
  • 1_3Life history & ecology
  • 1_4Harvest, use & livelihoods
  • 1_5Threats
  • 1_6Actions
  • 2_2Area-based Management Plan
  • 2_3Harvest & Trade Management Plan
  • 3_1Population trends
Niche IUCN globaleExpert

Royaumes biogéographiques

Palearctic

Systèmes (terrestre/eau douce/marin)

Terrestrial
Références bibliographiques (30)Expert
  1. IUCN. 2025. The IUCN Red List of Threatened Species. Version 2025-1. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 27 March 2025).
  2. Kojola, I., Henttonen, H., Heikkinen, S. and Ranc, N. 2023. Golden jackal expansion in northernmost Europe: records in Finland. <i>Mammalian Biology</i> https://doi.org/10.1007/s42991-023-00382-3.
  3. Männil, P. and Ranc, N. 2022. Golden jackal (<i>Canis aureus</i>) in Estonia: development of a thriving population in the boreal ecoregion. <i>Mammal Research </i> 67: 245-250.
  4. Lanszki, J., Hayward, M.W., Ranc, N. and Zalewski, A. 2022. Dietary flexibility promotes range expansion: the case of golden jackals in Eurasia. <i>Journal of Biogeography </i> 49: 993-1005.
  5. Ranc, N., Balys, V., Bučko, J., <i>et al</i>. 2022. Distribution of large carnivores in Europe 2012 - 2016: Distribution map for Golden Jackal (<i>Canis aureus</i>). <i>Zenodo [Data set]</i>: https://zenodo.org/doi/10.5281/zenodo.6382215
  6. Krofel, M., Hatlauf, J., Bogdanowicz, W., Campbell, L.A.D., Godinho, R., Jhala, Y.V., Kitchener, A.C., Koepfli, K.-P., Moehlman, P., Senn, H., Sillero-Zubiri, C., Viranta, S., Werhahn, G. and Alvares, F. 2022. Towards resolving taxonomic uncertainties in wolf, dog and jackal lineages of Africa, Eurasia and Australasia. <i>Journal of Zoology </i> 316: 155–168. DOI: 10.1111/jzo.12946.
  7. Sørensen, O.J. and Lindsø, L.K. 2021. Gullsjakal påvist i Norge – forvaltningsutfordringer ved nye arter i landet. <i>Fauna </i> 3-4: 74-87.
  8. Tillmann, J.E. 2020. Der Goldschackal in Deutschland. <i>Naturschutz und Landschaftsplanung </i> 52: 428-434.
  9. Guimarães, N., Bučko, J. and Urban, P. 2019. The rise of a carnivore, the evolution of the presence of the golden jackal in Slovakia. <i>Folia Zoologica </i> 68(2): 66-71.
  10. LCIE. In prep. Guidelines for Population Level Management Plans for Large Carnivores. Instituto di Ecologia Applicata, Rome.
  11. Jirků, M., Dostál, D., Robovský, J. and Šálek, M. 2018. Reproduction of the golden jackal (<i>Canis aureus</i>) outside current resident breeding populations in Europe: Evidence from the Czech Republic. <i>Mammalia</i>: 1864-1547.
  12. Trbojević, I. 2018. Distribution, status and management of Brown Bear (<i>Ursus arctos</i> L., 1758) in Bosnia and Herzegovina. <i>"From Mountains to Deep Seas”, 27th Rufford Small Grants Conference. Bar, Montenegro</i>: 32.
  13. Lanszki, J., Schally, G., Heltai, M. and Ranc, N. 2018. Golden jackal expansion in Europe: First telemetry evidence of a natal dispersal. <i>Mammalian Biology</i> 88: 81-84.
  14. Viranta, S., Atickem, A., Werdelin, L. and Stenseth, N.C. 2017. Rediscovering a forgotten canid species. <i>BMC Zoology</i> 2: 6.
  15. Krofel, M., Giannatos, G., Ćirovič, D., Stoyanov, S. and Newsome, T. 2017. Golden jackal expansion in Europe: a case of mesopredator release triggered by continent-wide wolf persecution? <i>Hystrix, the Italian Journal of Mammalogy</i> 28(1): 9-15.
  16. Newsome, T.M., Greenville, A.C., Ćirović, D., Dickman, C.R., Johnson, C.N., Krofel, M., Letnic, M., Ripple, W.J., Ritchie, E.G., Stoyanov, S. and Wirsing, A.J. 2017. Top predators constrain mesopredator distributions. <i>Nature Communications</i> 8: 15469.
  17. Hatlauf, J., Heltai, M., Szabó, L. and Hackländer, K. 2017. Golden Jackal (<i>Canis aureus</i>) occurrence in Austria: from first records to recent findings. <i>33rd International Union of Game Biologists Congress</i> IUGB, Montpellier 2017: 178.
  18. Urban, P., Bučko, J. and Guimarães, N. 2016. Golden jackal (<i>Canis aureus</i>) a booming species in Slovakia? <i>Zoologia 2016</i>.
  19. Lapini, L., Caldana, M. and Amori, G. 2016. Evolution and trends of the populations of <i>Canis aureus moreoticus</i> in Italy. X Italian Congress of Theriology. Viterbo, Italy.
  20. Ćirović, D., Penezić, A. & Krofel, M. 2016. Jackals as cleaners: Ecosystem services provided by a mesocarnivore in human-dominated landscapes. <i>Biological Conservation</i> 199: 51-55.
  21. Hatlauf, J. and Hackländer, K. 2016. Preliminary results for golden jackal (<i>Canis aureus</i>) survey in Austria. <i>Gesellschaft für Wildtier- und Jagdforschung e.V. (GWJF). Beiträge zur Jagd- und Wildforschung</i> 41: 295-306.
  22. Kapota, D., Dolev, A., Bino, G., Yosha, D., Guter, A., King, R. and Saltz, D. 2016. Determinants of emigration and their impact on survival during dispersal in fox and jackal populations. <i>Scientific reports</i> 6.
  23. Penezić, A. and Ćirović, D. 2015. Seasonal variation in diet of the golden jackal (<i>Canis aureus</i>) in Serbia. <i>Mammal Research</i> 60(4): 309-317.
  24. Trouwborst, A., Krofel, M. and Linnell, J.D.C. 2015. Legal implications of range expansions in a terrestrial carnivore: the case of the golden jackal (<i>Canis aureus</i>) in Europe. <i>Biodiversity and Conservation</i> 24: 2593-2610.
  25. Galov, A., Fabbri, E., Caniglia, R., Arbanasić, H., Lapalombella, S., Florijančić, T., Bošković, I., Galaverni, M. and Randi, E. 2015. First evidence of hybridization between Golden Jackal (<i>Canis aureus</i>) and domestic dog (<i>Canis familiaris</i>) as revealed by genetic markers. <i>Royal Society Open Science</i> 2: 150450.
  26. Kowalczyk, R., Wudarczyk, M., Wójcik, J. and Okarna, H. 2015. Northernmost record of reproduction of the expanding golden jackal population. <i>Mammalian Biology </i> 100(1): 107-111.
  27. Rutkowski, R., Krofel, M., Giannatos, G., Ćirović, D., Männil, P., Volokh, A., Lanszki, J., Heltai, M., Szabo, L., Banea, O., Yavruyan, E., Hayrapetyan, V., Kopaliani, N., Miliou, A., Tryfonopoulos, G., Lymberakis, P., Penezić, A., Pakeltytė, G., Suchecka, E. and Bogdanowicz, W. 2015. A European Concern? Genetic Structure and Expansion of Golden Jackals (<i>Canis aureus</i>) in Europe and the Caucasus. <i>PLoS ONE</i> 10(11):e0141236.
  28. Kowalczyk, R., Kołodziej-Sobocińska, M., Ruczyńska, I. and Wójcik, J. 2015. Range expansion of the golden jackal (<i>Canis aureus</i>) into Poland: first records. <i>Mammal Research</i> 60(4): 411-414.
  29. Chapron, G., Kaczensky, P., Linnell, J.D.C., von Arx, M., Huber, D., Andrén, H., Vicente López-Bao, J., Adamec, M., Álvares, F., Anders, O., Balčiauskas, L., Balys, V., Bedő, P., Bego, F., Blanco, J. C., Breitenmoser, U., Brøseth, H., Bufka, L., Bunikyte, R., Ciucci, P., Dutsov, A., Engleder, T., Fuxjäger, C., Groff, C., Holmala, K., Hoxha, B., Iliopoulos, Y., Ionescu, O., Jeremić, J., Jerina, K., Kluth, Knauer, F., Kojola, I., Kos, I., Krofel, M., Kubala, J., Kunovac, S., Kusak, J., Kutal, M., Liberg, O., Majić, A., Männil, P., Manz, R., Marboutin, E., Marucco, F., Melovski, D., Mersini, K., Mertzanis, Y., Mysłajek, R.W., Nowak, S., Odden, J., Ozolins, J., Palomero, G., Paunović, M., Persson, J., Potočnik, H., Quenette, P.-Y., Rauer, G., Reinhardt, I., Rigg, R., Ryser, A., Salvatori, V., Skrbinšek, T., Stojanov, A., Swenson, J.E., Szemethy, L., Trajçe, A., Tsingarska-Sedefcheva, E., Váňa, M., Veeroja, R., Wabakken, P., Wölfl, M., Wölfl, S., Zimmermann, F., Zlatanova, D., and Boitani, L. 2014. Recovery of Large carnivores in Europe's modern human-dominated landscapes. <i>Science</i> 346: 1517-1519.
  30. Fabbri, E., Caniglia, R., Galov, A., Arbanasić, H., Lapini, L., Bošković, I., Florijančić, T., Vlasseva, A., Ahmed, A., Mirchev, R. L. and Randi, E. 2014. Genetic structure and expansion of golen jackals (<i>Canis aureus</i>) in the north-western distribution range (Croatia and Italian Alps). <i>Conservation Genetics</i> 15: 187-199.
Évaluateurs & contributeurs (4)Expert
assessor
Ranc, N., Krofel, M. & Ćirović, D.
contributor
Acosta-Pankov, I., Balys, V., Banea, O., Beatham, S., Beneš, J., Berce, M., Berce, T., Bučko, J., Csanyi, S., Filacorda, S., Giannatos, G., Guimaraes, N., Hatlauf, J., Heltai, M., Ionescu, G., Ionescu, O., Ivanov, G., Jansman, H., Kowalczyk, R., Kryštufek, B., Kunz, F., Kutal, M., Lamut, S., Lanszki, J., Lapini, L., Männil, P., Melovski, D., Migli, D., Mladenović, J., Molinari, P., Muhaxhiri, J., Olsen, K., Ozoliņš, J., Pavanello, M., Popa, M., Pyšková, K., Reinhardt, I., Šálek, M., Schally, G., Selanec, I., Shkvyria, M., Stankov, S., Stojanov, A., Sunde, P., Szabó, L., Tarman, J., Trajçe, A., Trbojević, I., Urban, P., Valeriu, C., Veeroja, R., Yakovlev, Y. & Zimmermann, F.
evaluator
Hoffmann, M., Battistoni, A. & Chiozza, F.
institutions
IUCN SSC Large Carnivore Initiative for Europe

Ranc, N., Krofel, M. & Ćirović, D. 2025. Canis aureus (Europe assessment). The IUCN Red List of Threatened Species 2025: e.T118264161A214278675. Accessed on 05 May 2026.

Traits biologiques

21 valeurs · 8 sources

Morphologie(4)

Masse adulte
11 kg
AnAge
Longueur
-999 mm
PanTHERIA
Masse naissance
208 g
AnAge
Masse au sevrage
-999000 mg
PanTHERIA

Cycle de vie(1)

Longévité max
19 ans
AnAge
Voir 16 traits de plus (3 catégories)

Reproduction(6)

Maturité sexuelle
11 mois
AnAge
Gestation
2,1 mois
AnAge
Intervalle naissances
1 ans
AnAge
Taille de portée
3
AnAge
Portées par an
1
AnAge
Sevrage
2,5 mois
AnAge

Écologie & habitat(9)

Fruits (%)
10 %
elton_mammals
Invertébrés (%)
10 %
elton_mammals
Nectar (%)
0 %
elton_mammals
Autre végétal (%)
0 %
elton_mammals
Charognard (%)
0 %
elton_mammals
Graines (%)
0 %
elton_mammals
Vert. ectothermes (%)
10 %
elton_mammals
Vert. endothermes (%)
50 %
elton_mammals
Poissons (%)
10 %
elton_mammals

Divers(1)

Température corporelle
38,8 °C
AnAge

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

Chant

12 captations · Xeno-canto
chantA
47s
cri socialA
1:26
cri d’alarmeA
8s
uncertainA
2:39
enregistrementA
1:52
Voir 7 captations de plus
chantA
31s
criA
42s
enregistrementB
55s
chantA
19s
criB
1:09
enregistrementB
54s
chantA
18s

Hot-link CDN Xeno-canto. Chaque captation porte sa propre licence Creative Commons (visible quand la piste est active) et l'attribution de son auteur.

Consulter sur les bases externes

Observations & statuts

Cartographie

Bibliographie

Note nomenclaturale & synonymesExpert

Note nomenclaturale

TAXREF v18 — INPN/MNHN

Synonymes (65)— redirigent vers cette page

  • Aureus aureusLinnaeus, 1758
  • Canis anthusF. Cuvier, 1820
  • Canis anthus soudanicusThomas, 1903
  • Canis aureus algirensisWagner, 1841
  • Canis aureus anthusF. Cuvier, 1820
  • Canis aureus aureusLinnaeus, 1758
  • Canis aureus balcanicusBrusina, 1892
  • Canis aureus beaHeller, 1914
  • Canis aureus cruesemanniMatschie, 1900
  • Canis aureus ecsedensis(Kretzoi, 1947)
  • Canis aureus hungaricusEhik, 1938
  • Canis aureus indicusHodgson, 1833
  • Canis aureus minorEhik, 1938
  • Canis aureus moreoticaI. Geoffroy Saint-Hilaire, 1835
  • Canis aureus nariaWroughton, 1916
  • Canis aureus qattarensisSaleh & Basuony, 2014
  • Canis aureus ripariusHemprich & Ehrenberg, 1832
  • Canis aureus soudanicusThomas, 1903
  • Canis aureus syriacusHemprich & Ehrenberg, 1833
  • Canis aureus typicusKolenati, 1858
  • Canis aureus var. algiraKolenati, 1858
  • Canis aureus var. barbarusKolenati, 1858
  • Canis aureus var. caucasicaKolenati, 1858
  • Canis aureus var. indicaKolenati, 1858
  • Canis aureus var. moreoticaI. Geoffroy Saint-Hilaire, 1835
  • Canis aureus var. nubicaKolenati, 1858
  • Canis aureus var. senegalensisKolenati, 1858
  • Canis aureus var. syriacoKolenati, 1858
  • Canis aureus vulgarisWagner, 1841
  • Canis barbarus(Hamilton Smith, 1839)
  • Canis cruesemanniMatschie, 1900
  • Canis dalmatinusWagner, 1841
  • Canis gallaensisLorenz, 1906
  • Canis graecusWagner, 1841
  • Canis hadramaticusNoack, 1896
  • Canis indicusHodgson, 1833
  • Canis indicus kolaWroughton, 1916
  • Canis lankaWroughton, 1916
  • Canis lupaster doederleiniSaleh and Basuony, 2014
  • Canis mengesiNoack, 1897
  • Canis nariaWroughton, 1916
  • Canis ripariusHemprich and Ehrenberg, 1833
  • Canis sacerHemprich and Ehrenberg, 1833
  • Canis somalicusLorenz, 1906
  • Canis studeriHilzheimer, 1906
  • Canis syriacusHemprich and Ehrenberg, 1830
  • Canis thooidesHilzheimer, 1906
  • Canis variegatusCretzschmar, 1826
  • Sacalius aureusHamilton Smith, 1839
  • Sacalius indicusHamilton Smith, 1839
  • Thos aureus
  • Thos aureus algirensisAllen, 1939
  • Thos aureus anthusAllen, 1939
  • Thos aureus beaHeller, 1914
  • Thos aureus ecsedensisKretzoi, 1947
  • Thos aureus lupasterAllen, 1939
  • Thos aureus maroccanusAllen, 1939
  • Thos aureus soudanicusAllen, 1939
  • Thos gallaensisAllen, 1939
  • Thos lampertiAllen, 1939
  • Thos lupaster maroccanusCabrera, 1921
  • Thous anthusHamilton Smith, 1839
  • Thous sengalensiHamilton Smith, 1839
  • Thous variegatusHamilton Smith, 1839
  • Vulpes indiae orientalisLinnaeus, 1758

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