
Chat des sables
Felis margaritaLoche, 1858
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Description
chat vivant principalement dans les déserts
Source : Wikidata
Pays · région · aire protégée · écorégion · biome
Graphe en cours d’indexation
Calcul du tissu écologique de Felis margarita.
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Liste rouge IUCN
LC · Préoccupation mineure?Inconnue- Évaluation
- 2016 · v3.1
- Altitude
- – m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
There are relatively few records of Sand Cat and the species is often reported as rare (Sliwa 2013). It was recently recorded in isolated areas from where historical records do not exist, such as deserts in Syria, western Saudi Arabia, western Iraq and central Chad (Serra et al. 2007, Strauss et al. 2007, Mohammad et al. 2013, M. K. Mohammad, pers. obs. February 2016, Rabeil et al. 2016). However, recent records are lacking from several range countries such as from Jordan, Palestine, Qatar and Yemen (Banfield et al. 2014), where specific surveys have either not been conducted, or the species has not been detected due to its elusive habits or the species is absent and thus the conservation status of the Sand Cat is unknown there. In Israel, the species has not been recorded in the country on post-2000 surveys and is now considered locally extinct (Noam Leader, Israel Nature and Parks Authority, in litt. 2014).
The only available density estimates come from a telemetry study in southern Israel, where 11 Sand Cats were caught in the study area of 15 x 25 km (375 km²), resulting in an estimated density of 2.9/100 km² (M. Abbadi, in Sliwa 2013). Based on this density and the estimated AOO (based on only the extant species range), the total population is conservatively estimated at 27,264 mature individuals. In the Saja / Umm Ar-Rimth Protected Area, Saudi Arabia, the annual home ranges (95% MCP) of 7 Sand Cats were 19.6 – 50.7 km² (Sher Shah and Shobrak 2016 in prep). In the same area Sand Cats appear to occur at far lower densities than Rüppell's Fox Vulpes rueppellii (Strauss et al. 2007 and pers. comm. 2008). Sher Shah recorded 692 Rüppells Foxes in comparison to 62 Sand Cat captured in a total of 4509 trap nights between 2001-2009 (Sher Shah et al. 2016 in prep). Particularly in the years 2006-07 there was heightened mortality in the 5 captured and radio-collared Sand Cats, three (60%) of them dying within a few months and the remaining two recorded missing after making large movements away from their initial home ranges. This 100 % mortality could have been due to the drought conditions the protected areas experienced (Sher Shah and Shobrak 2016 in prep, Sher Shah et al. 2016 in prep). This is also reflected by live-trapping in Saja / Umm Ar-Rimth Protected Area, Saudi Arabia where six Sand Cats were caught in a trap grid in 2002 reaching a potential density of 16.66 /100 km² (Sher Shah and Shobrak 2016 in prep, Sher Shah et al. 2016 in prep). Subsequent trapping sessions in 2005 with seven Sand Cats caught gave such trapping derived densities at 14.27 / 100 km². The capture rate decreased to 2.83 / 100 km² in 2006 with only one caught. In the years 2007 and 2009 no Sand Cats were caught in the same trapping grid (Sher Shah and Shobrak 2016 in prep, Sher Shah et al. 2016 in prep), documenting a possible local decline. Whether such calculations are valid estimators of densities is open to debate. A certain decline in capture rate could also have been due to trap shyness. In Mahazat As-Sayd Reserve no Sand Cat was seen between 2008 and 2009 (P. Cunningham, pers. comm. 2016). In low-quality habitat, such as shifting sand dunes, densities may be very low (Sliwa 2013). Numbers may fluctuate in response to environmental conditions leading to prey declines and recoveries (Sunquist and Sunquist 2002). The Sand Cat population on the Arabian Peninsula is considered to be declining at an unknown rate (Mallon and Budd 2011, Banfield et al. 2014), although this is difficult to prove, while in certain areas there may be more Sand Cats than previously expected (T. Wacher, pers. comm. 2016). There are no confirmed records from Yemen.
In the past 10 years (2006-2016) there seem to be repeated and regular reports of Sand Cats from Western Sahara, South Algeria, Niger, Chad, southwestern Saudi Arabia and the border area of southeaster Saudi Arabia with Oman and the United Arab Emirates, and Iran, probably strongholds for the species. This contrasts with the status in Central Asia and Pakistan, which is largely unknown, with only very few recent records available (Burnside et al. 2014). The same applies to the Karakum desert in Turkmenistan, with no records within the past 25 years, most of the records being far older (cited in Heptner and Sludskii 1972) and thus at least 5 generations of Sand Cats ago.
The only available density estimates come from a telemetry study in southern Israel, where 11 Sand Cats were caught in the study area of 15 x 25 km (375 km²), resulting in an estimated density of 2.9/100 km² (M. Abbadi, in Sliwa 2013). Based on this density and the estimated AOO (based on only the extant species range), the total population is conservatively estimated at 27,264 mature individuals. In the Saja / Umm Ar-Rimth Protected Area, Saudi Arabia, the annual home ranges (95% MCP) of 7 Sand Cats were 19.6 – 50.7 km² (Sher Shah and Shobrak 2016 in prep). In the same area Sand Cats appear to occur at far lower densities than Rüppell's Fox Vulpes rueppellii (Strauss et al. 2007 and pers. comm. 2008). Sher Shah recorded 692 Rüppells Foxes in comparison to 62 Sand Cat captured in a total of 4509 trap nights between 2001-2009 (Sher Shah et al. 2016 in prep). Particularly in the years 2006-07 there was heightened mortality in the 5 captured and radio-collared Sand Cats, three (60%) of them dying within a few months and the remaining two recorded missing after making large movements away from their initial home ranges. This 100 % mortality could have been due to the drought conditions the protected areas experienced (Sher Shah and Shobrak 2016 in prep, Sher Shah et al. 2016 in prep). This is also reflected by live-trapping in Saja / Umm Ar-Rimth Protected Area, Saudi Arabia where six Sand Cats were caught in a trap grid in 2002 reaching a potential density of 16.66 /100 km² (Sher Shah and Shobrak 2016 in prep, Sher Shah et al. 2016 in prep). Subsequent trapping sessions in 2005 with seven Sand Cats caught gave such trapping derived densities at 14.27 / 100 km². The capture rate decreased to 2.83 / 100 km² in 2006 with only one caught. In the years 2007 and 2009 no Sand Cats were caught in the same trapping grid (Sher Shah and Shobrak 2016 in prep, Sher Shah et al. 2016 in prep), documenting a possible local decline. Whether such calculations are valid estimators of densities is open to debate. A certain decline in capture rate could also have been due to trap shyness. In Mahazat As-Sayd Reserve no Sand Cat was seen between 2008 and 2009 (P. Cunningham, pers. comm. 2016). In low-quality habitat, such as shifting sand dunes, densities may be very low (Sliwa 2013). Numbers may fluctuate in response to environmental conditions leading to prey declines and recoveries (Sunquist and Sunquist 2002). The Sand Cat population on the Arabian Peninsula is considered to be declining at an unknown rate (Mallon and Budd 2011, Banfield et al. 2014), although this is difficult to prove, while in certain areas there may be more Sand Cats than previously expected (T. Wacher, pers. comm. 2016). There are no confirmed records from Yemen.
In the past 10 years (2006-2016) there seem to be repeated and regular reports of Sand Cats from Western Sahara, South Algeria, Niger, Chad, southwestern Saudi Arabia and the border area of southeaster Saudi Arabia with Oman and the United Arab Emirates, and Iran, probably strongholds for the species. This contrasts with the status in Central Asia and Pakistan, which is largely unknown, with only very few recent records available (Burnside et al. 2014). The same applies to the Karakum desert in Turkmenistan, with no records within the past 25 years, most of the records being far older (cited in Heptner and Sludskii 1972) and thus at least 5 generations of Sand Cats ago.
Menaces identifiées(8 menaces classées CMP-IUCN)
11_2DroughtsOngoing1_1Housing & urban areasOngoing2_3_1Nomadic grazingOngoing5_1_2Unintentional effects (species is not the target)Ongoing5_1_3Persecution/controlOngoing8_1_2Named speciesFuture8_1_2Named speciesFuture8_2Problematic native species/diseasesOngoing
Description complète des menacesTexte détaillé évaluation IUCNExpert
Habitat degradation and loss for example through fencing (Sher Shah and Cunningham 2008, Banfield et al. 2014) are considered to be the major threats to the Sand Cat. Many areas are also more heavily frequented by humans, their domestic animals and commensals (i.e. red fox, Vulpes vulpes). Vulnerable arid ecosystems are being rapidly converted by infrastructural development and human settlement and activity, especially degraded through livestock grazing (Allan and Warren 1993, Al-Sharhan et al. 2003, Ghadirian et al. 2016). Degradation of desert ecosystems continues to be widely acknowledged as an urgent conservation problem (Bunaian et al. 2001, Abahussain et al. 2002, Al-Sharhat et al. 2003, Mallon and Budd 2011, Sliwa et al. 2013) and could result in a decline of Sand Cat populations, caused by a declining prey base. The Sand Cat's small mammal prey base depends on having adequate vegetation, and may experience large fluctuations due to drought (Sunquist and Sunquist 2002, Sher Shah and Shobrak 2016 in prep), or declines due to desertification and loss of natural vegetation. In the Arabian Peninsula, sand dune habitat continues to decline (Mallon and Budd 2011). Human induced habitat destruction through underground nuclear tests in the late 1990ies in Pakistan, where Sand Cats were recorded in the 1960ies. Several of the areas have been affected by political strife, and war-like conditions that have accelerated habitat destruction. Habitat destruction through civil war i.e. in Syria. In Iraq, the location which the Sand Cat was recorded from (Mohammad et al. 2013) falls within the Arabian Desert and East Sahero-Arabian Xeric Shrublands (PA1303) which is considered to be “Critical/Endangered” (Republic of Iraq Ministry of Environment 2010, M. K. Mohammad pers. comm. 2016).
More recently, additional threats identified are the introduction of feral and domestic dogs and cats, creating direct competition for prey and through predation and disease transmission (Nowell and Jackson 1996, Ostrowski et al. 2003, Sliwa 2013, Sliwa et al. 2013). This applies particularly along roads through suitable habitat (Sliwa et al. 2013, Sliwa, pers. obs. 2015). They are also killed in traps laid out by inhabitants of oases targeting Red Fox, Rüppel’s Fox and Golden Wolf (jackal) Canis anthus or in retaliation for killing their chickens or Houbara and MacQueen's bustard Chlamydotis undulata / Ch. macqueenii (De Smet 1989, Dragesco-Joffé 1993). Locally, Sand Cats may be threatened by the pet trade (Banfield et al. 2014, P. Cunningham pers. comm. 2016). In Iran, Sand Cats are reported to get killed by shepherd dogs and trapped in snares set for other species (Ghadirian et al. 2016). They also get stuck in fences (Sher Shah and Cunningham 2008) and are vulnerable to indiscriminate trapping and poisoning of predators (Mallon and Budd 2011). There are occasional reports of Sand Cats shot in Saudi Arabia (M. Strauss pers. comm. 2008, Cunningham 2009).
More recently, additional threats identified are the introduction of feral and domestic dogs and cats, creating direct competition for prey and through predation and disease transmission (Nowell and Jackson 1996, Ostrowski et al. 2003, Sliwa 2013, Sliwa et al. 2013). This applies particularly along roads through suitable habitat (Sliwa et al. 2013, Sliwa, pers. obs. 2015). They are also killed in traps laid out by inhabitants of oases targeting Red Fox, Rüppel’s Fox and Golden Wolf (jackal) Canis anthus or in retaliation for killing their chickens or Houbara and MacQueen's bustard Chlamydotis undulata / Ch. macqueenii (De Smet 1989, Dragesco-Joffé 1993). Locally, Sand Cats may be threatened by the pet trade (Banfield et al. 2014, P. Cunningham pers. comm. 2016). In Iran, Sand Cats are reported to get killed by shepherd dogs and trapped in snares set for other species (Ghadirian et al. 2016). They also get stuck in fences (Sher Shah and Cunningham 2008) and are vulnerable to indiscriminate trapping and poisoning of predators (Mallon and Budd 2011). There are occasional reports of Sand Cats shot in Saudi Arabia (M. Strauss pers. comm. 2008, Cunningham 2009).
Habitats préférentiels (classification IUCN)
8_1Desert - Hot★
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
Included on CITES Appendix II. Hunting of this species is prohibited in Algeria, Iran, Israel, Kazakhstan, Mauritania, Niger, Pakistan, Tunisia, and United Arab Emirates (Nowell and Jackson 1996). On the African continent, the Sand Cat inhabits several protected areas, including Tassili n'Ajjer and Ahaggar Cultural Parks (Algeria), Aïr and Ténéré National Reserve (Niger), and possibly Djebel Bou-Hedma Biosphere Reserve (Tunisia) (Sliwa 2013). In Iran, it has been reported from the Abbasabad Naein Reserve, Kavir and Touran National Park (Semnan Province), Shaskooh and Mozaffari protected areas, Siahkooh National Park (Yazd province) and in Moteh and Touran protected areas (Ghadirian et al. 2016, Farhadinia et al. 2008, Nowell and Jackson 1996). On the Arabian Peninsula, the Sand Cat was recorded in the protected areas of Mahazat As-Sayd (not in 2008/9), Saja/Umm Ar-rimth and Uruq Bani Ma'arid, Harrat al Harrah Reserve (Saudi Arabia), in the Wadi Rum (Jordan), and in Baynunah and Umm Al Zumul Reserves (UAE) (Strauss pers. obs., Mallon and Budd 2011, Banfield et al. 2014).
Captive breeding populations exist in the range countries at Al Wabra (Qatar), The Scientific Centre (Kuwait), Al Ain Zoo, and the Breeding Centre for Endangered Arabian Wildlife (UAE), Omani Wild Animals Breeding Centre (Oman), Zoological Center Tel Aviv-Ramat Gan, Hai Bar Yotvata NR, I. Meier Segals Garden for Zoological Research, Tel Aviv (Israel). There are also captive breeding populations in the USA and Europe (Breton 2015).
The development of reliable survey methods is urgently needed (Mallon and Budd 2011). Furthermore, studies on the behaviour and ecology of the Sand Cat are crucial to apply appropriate conservation measures.
Captive breeding populations exist in the range countries at Al Wabra (Qatar), The Scientific Centre (Kuwait), Al Ain Zoo, and the Breeding Centre for Endangered Arabian Wildlife (UAE), Omani Wild Animals Breeding Centre (Oman), Zoological Center Tel Aviv-Ramat Gan, Hai Bar Yotvata NR, I. Meier Segals Garden for Zoological Research, Tel Aviv (Israel). There are also captive breeding populations in the USA and Europe (Breton 2015).
The development of reliable survey methods is urgently needed (Mallon and Budd 2011). Furthermore, studies on the behaviour and ecology of the Sand Cat are crucial to apply appropriate conservation measures.
Actions de conservation (1)Conservation Actions Classification Scheme — IUCNExpert
1_1Site/area protection
Stress écologiques (11)Stresses Classification — IUCNExpert
1_1Ecosystem conversion1_1Ecosystem conversion1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation2_1Species mortality2_1Species mortality2_1Species mortality2_1Species mortality2_3_7Reduced reproductive success
Priorités de recherche (5)Research Needed Classification — IUCNExpert
1_2Population size, distribution & trends1_3Life history & ecology1_5Threats1_6Actions3_1Population trends
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
AfrotropicalPalearctic
Systèmes (terrestre/eau douce/marin)
Terrestrial
Références bibliographiques (30)Sources scientifiques de l'évaluation IUCNExpert
- 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).
- Rabeil, T., Wacher, T. and Newby, J. 2016. Sand cat sightings in Niger and Chad. <i>Cat News</i> 63 (in press).
- Breton, G., Sliwa, A., Azizi, S. and Essalhi, A. 2016. Sand cats in the Moroccan Sahara, preliminary results if a new study. <i>Cat News</i> 63 (in press).
- Ghadirian, T., Akbari, H., Mohammadreza, B., Ghoddousi, A., Hamidi, A., Kh. and Dekhordi M.E. 2016. Sand cat in Iran: present status, distribution and conservation challenges. <i>Cat News Special Issue</i> 10 (in press).
- Rodríguez-Siles, J., Arredondo Acero, A., Díaz-Portero, M.A., Herrera-Sánchezm J.F., Valenzuela Serrano, G., Sáez, J.M., García-Cardenete, L. and Varillas, B. 2015. Recherche de faune à L'OUed Afra (Massiv Aydar) et à L'Oued Khat: Harmusch - mission Décembre.
- Breton, G. 2015. <i>Sand Cat (Felis margarita) International Studbook Volume XXII, current to 31 December 2014. WAZA / Le Parc des Félins</i>.
- Chevallier, J., Goyaud, C. and Boutin, J. 2014. Voyage naturaliste au Sahara Occidental du 26 Mars au 9 avril 2014.
- Banfield L.M., al Qahtani H. and Mallon D. 2014. Arabian Sand Cat <i>Felis margarita harrisoni</i> Status Reveiw and Conservation Strategy. Al Ain Zoo, Abu Dhabi, United Arab Emirates.
- Burnside, R.B., Koshkin, M. and Dolman, P.M. 2014. Breeding population of sand cat in the Southern Kyzylkum Desert, Uzbekistan. <i>Cat News</i> 60: 25-26.
- Mohammad, M.K., Lahony S.R. and Al-Rammahi H.M. 2013. First record of the Sand cat, <i>Felis margarita</i> Loche, 1858 (Mammalia: Carnivora, Felidae), from Iraq. <i>Zoology in the Middle East</i> 59(4): 358-359.
- 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.
- Sliwa, A., Breton, G. & Chevalier, F. 2013. Sand cat sightings in the Moroccan Sahara. <i>Cat News</i> 59: 28-30.
- Sliwa, A. 2013. <i>Felis margarita</i>. In: J. S. Kingdon and M. Hoffmann (eds), <i>The Mammals of Africa</i>, Academic Press, Amsterdam, The Netherlands.
- Chevalier, F., Thevenot, M. and Bergier, P. 2012. Notes sur quelques mammifères terrestres observés près de Dakhla, Oued Ad-Deheb . <i>Go-South Bull.</i> 9: 1-6.
- Webb, R., Blincow, J. and Goodgame, N. 2012. Saharan predators. Field report Morocco & Western Sahara 15-26 December 2012.
- Breitenmoser, Ch. and Breitenmoser U. (eds.). 2011. <i>Cats of the World</i>. Stämpfli Publikationen AG, Bern.
- Mallon D. and Budd. K. 2011. Regional Red List Status of Carnivores in the Arabian Peninsula. IUCN and Sharjah, UAE: Environment and Protected Areas Authority, Cambridge, UK and Gland, Switzerland.
- Republic of Iraq Ministry of Environment. 2010. Iraq 4th National report to the Convention on Biological Diversity (CBD) 2010.
- Cunningham, P.L. 2009. Persecution of Rüppell’s fox in central Saudia Arabia. <i>Canid News</i> 12: 1-5.
- Belbachir, F. 2009. Spotted: the elusive sand cat in Algerian Ahaggar Mountains, central Sahara. <i>Cat News</i> 50: 17-18.
- Farhadinia, M.S., Akbari, H., Beheshti, M., Sadeghi, A. and Halvani, M.R. 2008. Felids of Abbasabad Naein Reserve, Iran. <i>Cat News</i> 48: 14-16.
- Sher Shah, M. and Cunningham, P. 2008. Fences as a threat to Sand cats <i>Felis margarita</i> Loche, 1958, in Saudi Arabia. <i>Zoology in the Middle East</i> 42: 99-101.
- Strauss, W. M., Shobrak, M. and Sher Shah, M. 2007. First trapping results from a new sand cat study in Saudi Arabia. <i>Cat News</i> 47: 20-21.
- O'Brien, S.J. and Johnson, W.E. 2007. The evolution of cats. <i>Scientific American</i> July: 68-75.
- Serra, G., Abdallah, M.S. and Al Quaim, G. 2007. Occurrence of Ruppell's fox <i>Vulpes rueppelli</i> and Sand cat <i>Felis margarita</i> in Syria. <i>Zoology in the Middle East</i> 42: 99-101.
- Johnson, W.E., Eizirik, E., Pecon-Slattery, J., Murphy, W.J., Antunes, A., Teeling, E. and O'Brien, S.J. 2006. The late Miocene radiation of modern Felidae: A genetic assessment. <i>Science</i> 311: 73-77.
- Habibi, K. 2004. <i>Mammals of Afghanistan</i>. Zoo Outreach Organisation/USFWS, Coimbatore, India.
- Al-Sharhan, A.S., Wood, W.W., Goudie, A.S., Fowler, A. and Abdellatif, E.M. 2003. <i>Desertification in the Third Millennium</i>. Swets and Zeltinger, Lisse, Netherlands.
- Otrowski, S., Van Vuuren, M., Lenain, D.M. and Durand, A. 2003. A serologic survey of wild felids from central west Saudi Arabia. <i>Journal of Wildlife Diseases</i> 39: 696-701.
- Abahussain, A.A., Abdu, A.S., Al-Zubari, W.K., El-Deen, N.A. and Abdul-Raheem, M. 2002. Desertification in the Arab region: analysis of current status and trends. <i>Journal of Arid Environments</i> 51: 521-545.
Évaluateurs & contributeurs (4)Personnes ayant contribué à l'évaluation IUCNExpert
assessor
Sliwa, A., Ghadirian, T., Appel, A., Banfield, L., Sher Shah, M. & Wacher, T.
contributor
Gritsina, M., Breton, G., Belbachir, F., Mohammad, K.M., Burnside, J., Duckworth, J.W., Spalton, A., Manati, A., Cunningham, P., Amr, Z.S.S., Gil Sánchez, J. & Strauss, M.
evaluator
Nowell, K., Hunter, L., Hoffmann, M., Breitenmoser-Würsten, C., Lanz, T., Breitenmoser, U. & Mallon, D.
facilitators
Lanz, T. & Breitenmoser-Würsten, C.
Sliwa, A., Ghadirian, T., Appel, A., Banfield, L., Sher Shah, M. & Wacher, T. 2016. Felis margarita. The IUCN Red List of Threatened Species 2016: e.T8541A50651884. Accessed on 05 May 2026.
Traits biologiques
20 valeurs · 6 sources
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
Calcul de la distribution GBIF· ~10–60 s
Phénologie
Calcul du calendrier d'apparition· ~5–30 s
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