Please note, this National Red List website contains a subset of data whilst we transition to national focal point driven data uploads. We thank you for your patience with this and welcome national contributors to get in touch to update their national dataset. Terms of Use including citation guidance are found here.

The previous dataset is available via: https://archive.nationalredlist.org/. This site is no longer updated but can help with most enquiries whilst we focus on redevelopment.

Assessment ID
330660
Taxon name
Asellia tridens
(E. Geoffroy, 1813)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Asellia tridens
(E. Geoffroy, 1813)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
chiroptera
Family
hipposideridae
Genus
Asellia
Species
tridens
Species authority
(E. Geoffroy, 1813)
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Data deficient
Abbreviated status
DD
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This species had been recorded in large numbers in the 1950s in two areas in UAE (Sharjah city and the Al Ain area) but is only known in small numbers from recent records. It is assessed as Data Deficient because too little is know about the current status and it is difficult to interpret the apparent decline in numbers since the 1950s. No regional adjustment is made to the Data Deficient assessment.
Assessment details
Year assessed
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species was recorded in large numbers in the 1950s. Several hundred individuals were observed, and several collected, in falaj (irrigation) tunnels at Al Ain in 1953 and numbers were seen flying out of old buildings in Sharjah city towards the airfield in July 1954 (Harrison 1955). It was next recorded in 2005 when a dead individual, apparently hit by a car, was found in a tree-lined road in Al Ain, and again in 2015 when a few live individuals were observed in a cave at Ain al Waal at the bottom of Jebel Hafeet (Judas et al. 2018). There was a new record in 2018 from the Fujairah and Ras Al Khaimah border area (J. Pereira pers. comm. 2018) and two were caught in a cave in western Fujairah during a survey in early 2018 (Jomat et al. 2018). The species is likely to be more widespread than these records indicate. Globally, the species ranges widely across North Africa south to Ethiopia and Somalia, the Arabian Peninsula and the Middle East, to Afghanistan and Pakistan (Monadjem et al. 2017b). It is quite widely distributed in Arabia (Harrison and Bates 1991).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
Habitat details as listed in assessment
In the UAE it is recorded roosting in buildings, falaj tunnels and caves. It is a colonial species that occupies crevices and cliffs in arid and semi-desert habitats, also roosting in caves, mines, and old tombs and buildings (Monadjem et al. 2017b).
Threats and conservation measures listed
Threats listed in assessment
Unknown. The increasing extent and intensity of urban lighting may have a negative impact on nocturnal flying invertebrates, the main prey base. Species in the mountains may be affected indirectly through falling water tables due to over-abstraction and reduced precipitation.
History
The backcasted 1996 assessment for this species is Data Deficient which matches the listing given by Hornby (1996).
Publication
Mallon, D., Hilton-Taylor, C., Allen, D., & Harding, K. (2019). UAE National Red List of Mammals: Marine and Terrestrial. A report to the Ministry of Climate Change and Environment, United Arab Emirates (p. 41). IUCN Global Species Programme. https://bit.ly/2RdZCQR
Assessment ID
330646
Taxon name
Felis silvestris
Schreber, 1777
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Felis silvestris
Schreber, 1777
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
carnivora
Family
felidae
Genus
Felis
Species
silvestris
Species authority
Schreber, 1777
Taxonomic notes and synonyms listed
There is currently no clear agreement on how to relate geographically linked variation in morphology and genetics to the taxonomy and systematics of the widely distributed Wildcat (Felis silvestris) (Kitchener and Rees 2009). The latest phylogeographical analyses (Driscoll et al. 2007, 2009; Macdonald et al. 2010) suggest that the Wildcat consists of five subspecific groups and three traditional subspecies (Nowell and Jackson 1996, Stuart et al. 2013): including the recent recognition of the Southern African Wildcat (F. s. cafra Desmarest, 1822). Based on genetic, morphological and archaeological evidence, the familiar housecat was believed to have been domesticated from the Near Eastern Wildcat (F. s. lybica), probably 9,000-“10,000 years ago in the Fertile Crescent region (Vigne et al. 2004, Driscoll et al. 2007), coinciding with the first agricultural settlements (Driscoll et al. 2007, Macdonald et al. 2010). Although the domestic cat derived relatively recently from the Wildcat, in terms of biological processes and phylogeny, it can be taxonomically classified either as a subspecies (F. s. catus) of F. silvestris or as a separate species (F. catus) (Macdonald et al. 2010). Recent evidence supports the classification of domestic cats as genetically distinct from Wildcats (Driscoll et al. 2007). For the purposes of this assessment, although we recognise the potential validity of the Southern African Wildcat (F. s. cafra), we defer to the species level until further research can accurately delineate subspecific geographical boundaries.
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
C2a(ii)
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This species is widely distributed in the UAE except in areas of sand dunes. It is very difficult to distinguish genuine wild animals from hybrids, but using records based on phenotypic appearance, the population size appears to be fairly small and probably in the range of 250-2,500 mature individuals. The species is undergoing continuing decline because of hybridisation with domestic cats, there is also some persecution, and loss of habitat to developments, and the species therefore qualifies for listing as Endangered (EN C2a(ii)). There is unlikely to be a significant rescue effect as the species is widely scattered and declining across the Arabian Peninsula and the borders are mostly fenced, except in higher parts of the mountains, which may impede or prevent cross-border movements.
Assessment details
Year assessed
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species is widely distributed in the UAE except in areas of sand dunes, but establishing details of the distribution is complicated by the presence of feral domestic cats and hybrids. Animals identified on the basis of phenotype have been recorded in Dubai Desert Conservation Reserve, Wadi Wurayah (camera-trapped in 2012 and 2015; Judas 2016), Hatta Conservation Area (camera-trapped in 2017; G. Feulner pers. comm.), Khor Kalba, and Jebel Hafeet (2017/2018). There are no recent records from surveys in the Abu Dhabi desert. Globally, the Wild Cat has a very broad distribution throughout most of Africa, Europe, and southwest and Central Asia, eastwards to India, China, and Mongolia (Yamaguchi et al. 2015). It was formerly widespread in the Arabian Peninsula but the current status and distribution are unclear due to the presence of many hybrids or feral cats (Mallon and Budd 1991).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
Habitat details as listed in assessment
Wild Cats occur in semi-desert, open plains, rocky terrain and mountain wadis, but are not found in the dunes and true desert areas (Harrison and Bates 1991, Aspinall et al. 2005). A male and female were radio-collared and tracked in the desert of Sharjah for 4 and 14 months respectively. The female had a home range of 51 km<sup>2</sup> and 42 den sites were recorded, many of them used repeatedly (Phelan and Sliwa 2005, 2006).
Threats and conservation measures listed
Threats listed in assessment
The major threat is hybridisation with feral and free-ranging domestic cats which are now widespread. Disease transfer from domestic cats is also a potential risk (Mallon and Budd 2011). Direct and indirect persecution also occurs, e.g. a burrow was found sealed and the Wild Cat inside suffocated by smoke (Phelan and Sliwa 2005, 2006). Overgrazing in some sites may have reduced vegetation cover and thereby the abundance of small mammals and other prey.
History
It is not clear what criteria would have been used in 1996 (Hornby 1996), but likely to have been assessed under criteria different than those currently applied by IUCN.
Publication
Mallon, D., Hilton-Taylor, C., Allen, D., & Harding, K. (2019). UAE National Red List of Mammals: Marine and Terrestrial. A report to the Ministry of Climate Change and Environment, United Arab Emirates (p. 41). IUCN Global Species Programme. https://bit.ly/2RdZCQR
Assessment ID
330159
Taxon name
Neophocaena phocaenoides
(G. Cuvier, 1829)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Neophocaena phocaenoides
(G. Cuvier, 1829)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
cetartiodactyla
Family
phocoenidae
Genus
Neophocaena
Species
phocaenoides
Species authority
(G. Cuvier, 1829)
Taxonomic notes and synonyms listed
The recognition of two externally distinct morphological forms of Finless Porpoises as separate biological species, the Indo-Pacific Finless Porpoise (Neophocaena phocaenoides) and the Narrow-ridged Finless Porpoise (N. asiaeorientalis), was accepted only recently when it was demonstrated that the two forms are reproductively isolated (and likely have been separated since the last glacial maximum) even though they occur sympatrically in a fairly large area of eastern Asia (Wang et al. 2008, Jefferson and Wang 2011). [Much of the literature published before ca 2010 refers to all Finless Porpoises (both species) as N. phocaenoides.] Differences in the external morphology of the dorsal aspect of the two species are distinguishable even amongst free-ranging animals (as opposed to only specimens in-hand) (Wang et al. 2010). Intermediates between the two main forms have never been reported even though several hundreds to thousands of carcasses have been examined. The two species also clearly differ in craniometry (Amano et al. 1992, Jefferson 2002). There is evidence to suggest subpopulation structure within Indo-Pacific Finless Porpoises in some areas (Jefferson 2002, Yang et al. 2008, Chen et al. 2010, Xu et al. 2010, Li et al. 2011, Ju et al. 2012, L. Li et al. 2013, S. Li et al. 2013, Jia et al. 2014, Lin et al. 2014) and this may apply throughout much of the species' distribution.
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
A2bc; C2a(i); D
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
Preen (2004) reported a 71% decline in small species of dolphins in the Arabian Gulf from 1986 to 1999, which included this species. There is no information available on decline rates in the individual species, so based on the assumption that they all declined equally it appears reasonable to infer a population reduction of &gt;50% for Neophocaena phocaenoides over the past three generations (45 years). The species, therefore, qualifies for assessment as Endangered (EN) under criterion A2bc. The reduction was due to a combination of pressures including declining habitat quality because of increasing coastal development, bycatch, collision with boats and declines in fish stocks. The decline is continuing but it is not possible to say if it is at the same rate. The species also qualifies for listing as EN under criterion C2a(i) and under criterion D as the population size is less than 250 mature individuals. The species might qualify for listing as Critically Endangered under criterion C2a(ii) if it is determined that the UAE animals are a single subpopulation. There is no rescue effect, as the species does not move that far; the species tends to be very localised in its occurrence.
Assessment details
Year assessed
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
All UAE records, apart from several from Dubai, are from the waters off western Abu Dhabi, with concentrations in the Marawah Island and Sila'a areas (Aspinall and Baldwin 1999). Collins et al. (2005) considered there to be a more or less contiguous distribution along the western and southern margins of the Arabian Gulf. Globally, the species occurs in a narrow strip of shallow (usually (<) 50 m deep) coastal marine waters, as well as some river mouths and estuaries, around the northern rim of the Indian and western Pacific Oceans eastwards to Indonesia and north to central Chinese waters (Wang and Reeves 2017).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
Habitat details as listed in assessment
The shallow channels between sandbanks and mangrove-lined islands, typical of western UAE waters, are apparently a favoured habitat. It has been seen close to shore off Dubai. Throughout its range, the Indo-Pacific Finless Porpoise favours shallow inshore waters, including mangrove areas, lagoons and estuaries (Pilleri and Gihr 1974, Reeves et al. 1997, Aspinall and Baldwin 1999, Preen 2004, Jefferson and Hung 2004) and this makes it particularly vulnerable to bycatch and anthropogenic impacts (Collins et al. 2005).
Threats and conservation measures listed
Threats listed in assessment
The main threats to cetaceans in UAE waters include: incidental mortality in trawl and drift nets, depletion of prey populations (due in part to commercial overfishing); ship and boat strikes, offshore oil and gas exploration; noise from shipping, submarine sonar and oil and gas rigs. A UAE Fisheries Resource Assessment Survey in 2002 found that fish stocks in the Gulf had declined by 60%. Inshore and shallow-water species are further threatened by entanglement in abandoned fishing gear; coastal development including port and harbour construction, dredging, land reclamation, residential and tourist development; pollution (oil and hydrocarbons) and damage to feeding grounds in seagrass beds and reefs. During surveys by EAD, a large number of dolphins were observed with scars that were attributed to propeller cuts, indicating that vessel strike is a major threat to dolphin populations in Abu Dhabi waters (EAD 2015). A lack of information on most species (e.g. population size and trend, the location of critical areas, and feeding ecology) hinders the development of appropriate conservation actions.
History
Hornby (1996) assessed the species as Critically Endangered. It is not clear what criteria would have been used in 1996, but likely to have been assessed under criteria different than those currently applied by IUCN, and we consider Endangered to be the appropriate backcasted category in 1996 (under criteria A2bc; C2a(i); D), as it appears that Hornby was not aware of the declines in the species between 1986 and 1999 as reported by Preen (2004).
Publication
Mallon, D., Hilton-Taylor, C., Allen, D., & Harding, K. (2019). UAE National Red List of Mammals: Marine and Terrestrial. A report to the Ministry of Climate Change and Environment, United Arab Emirates (p. 41). IUCN Global Species Programme. https://bit.ly/2RdZCQR
Assessment ID
329991
Taxon name
Balaenoptera omurai
Wada, Oishi & Yamada, 2003
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Balaenoptera omurai
Wada, Oishi & Yamada, 2003
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
cetartiodactyla
Family
balaenopteridae
Genus
Balaenoptera
Species
omurai
Species authority
Wada, Oishi & Yamada, 2003
Taxonomic notes and synonyms listed
Although it was only recently described (Wada et al. 2003), the separate species identity of Omura's Whale, Balaenoptera omurai, is now well established phylogenetically (Sasaki et al. 2006). It was formerly regarded as a pygmy form of Bryde's Whale (B. brydei/edeni), but it is not closely related to that group, lying outside the clade formed by the Sei Whale (B. borealis) and two forms of Bryde's Whales). The morphology of Omura's Whale is quite distinct from those of Bryde's Whales and other known baleen whales, but its colouration resembles that of the Fin Whale (B. physalus) while lacking lateral rostral ridges (Wada et al. 2003). To date (December 2017), the only genetically confirmed observations of living Omura's Whales are of 18 biopsied individuals in an apparently resident population off northwestern Madagascar (Cerchio et al. 2015). Specimens collected in 1976 in the Solomon Sea (Ohsumi 1978) and in 1978 in the eastern Indian Ocean (Ohsumi 1980) were originally taken under a scientific permit for Bryde's Whales and were subsequently genetically identified as Omura's Whales (Wada et al. 2003). LeDuc and Dizon (2002) genetically analysed specimens of small Bryde's Whales from the Bohol Sea, Philippines, and found that they segregated phylogenetically outside the Sei/Bryde's Whale clade and basal to B. edeni/B. borealis. From a comparison of the published phylogenies, Sasaki et al. (2006) concluded that these specimens corresponded to Omura's Whale. Yamada et al. (2008) identified 24 skulls from a whaling operation in the Philippines as Omura's Whales.
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Data deficient
Abbreviated status
DD
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The global range of this recently described species, Balaenoptera omurai, is poorly known, and no estimates of abundance are available. Within UAE waters, the species is recorded from a single unconfirmed stranding in Ras Al Khaimah in March 2018 (R. Brownell Jr. pers. comm. 2018). Given the scarcity of records of the species from the UAE plausible categories span from Critically Endangered to Least Concern, and hence following IUCN guidelines the species is assessed for the UAE national Red List as Data Deficient.No regional adjustment is made to the Data Deficient assessment.
Assessment details
Year assessed
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The occurrence of Omura's Whale in UAE waters is unconfirmed and very poorly known. One of the two stranded whales found in March 2018 at Ras Al Khaimah might be this species (R. Brownell Jr. pers. comm. 2018). There is one record from Iranian waters just in the Arabian Gulf (Ranjbar et al. 2016) and the next closest is from the Red Sea (Egypt), so it may be present off the east coast of the UAE.The global range of Omura's Whale requires further research because very few specimens have been confirmed to date. The type specimen was a stranded individual collected near Oyama in the southern Sea of Japan in 1998 (Wada et al. 2003). Confirmed specimens and suspected sightings recorded to date are listed by Cerchio et al. (2017). The only genetically confirmed population of living Omura's Whales to date occurs off northwestern Madagascar (Cerchio et al. 2015) on the shallow continental shelf, mainly in the 10-25 m depth range. Photographs of living whales taken off New Caledonia appear to show Omura's Whales, and there have also been suspected live sightings off eastern Australia. Omura's Whales are at least partially sympatric with Bryde's Whales and occur both in deep water and in inshore areas. All records to date have been between 35'°N and 35'°S. It is unclear whether Omura's Whale is mainly a coastal species or if a substantial oceanic population exists.
Is there a map available in assessment?
Not possible
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
Habitat details as listed in assessment
The diet, habitat, and ecology of Omura's Whales are not well known. Omura's Whales occur in both deep and shallow water, and are at least partly sympatric with Bryde's Whales.
Threats and conservation measures listed
Threats listed in assessment
Given its occurrence in shallow waters, it may be subject to entanglement or bycatch and vessel strikes. Because the species has only recently been described and its range is poorly known, it is not yet possible to assess the type, level or extent of any threats.
History
The backcasted 1996 assessment for this species is Data Deficient if its existence back then had been known.
Publication
Mallon, D., Hilton-Taylor, C., Allen, D., & Harding, K. (2019). UAE National Red List of Mammals: Marine and Terrestrial. A report to the Ministry of Climate Change and Environment, United Arab Emirates (p. 41). IUCN Global Species Programme. https://bit.ly/2RdZCQR
Assessment ID
329990
Taxon name
Acomys dimidiatus
(Cretzschmar, 1826)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Acomys dimidiatus
(Cretzschmar, 1826)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
rodentia
Family
muridae
Genus
Acomys
Species
dimidiatus
Species authority
(Cretzschmar, 1826)
Taxonomic notes and synonyms listed
Formerly considered a subspecies of Acomys cahirinus. See Musser and Carleton (2005) for details concerning the relationship between Acomys dimidiatus and A. cahirinus.
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Near threatened
Abbreviated status
NT
Qualifying criteria (if given)
B1b(iii)
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
Within the UAE, this species is restricted to rocky areas, primarily the Hajar Mountains, Jebel Hafeet and Qarn Nazwa. The extent of occurrence (EOO) is just over 6,000 km<sup>2</sup>, there is a continuing decline in the extent and quality of habitat due to a variety of threats, however, the number of locations is more than ten and the range is not severely fragmented, so it is assessed as Near Threatened (close to qualifying for a threatened category under criterion B1ab(iii)). There might be some rescue effect from populations in adjoining countries, particularly Oman, but this is not thought to be significant hence the regional assessment is not adjusted.
Assessment details
Year assessed
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species was first recorded for the UAE in 1971 at Jebel Faiyah, Sharjah, and then again in 1991 when a dead specimen was found by a road near Ghayl, Ra's al Khaimah. Subsequent surveys have shown that this species is quite widespread and numerous through the Hajar Mountains at lower elevations, particularly where Acacia tortilis is present. The species is also found on Jebel Hafeet, where it occurs at all elevations including barren rocks near the summit (Aspinall et al. 2005). It has also been recorded at several sites in Ras Al Khaimah (RAK Nature pers. comm. 2018) and on Qarn Nazwa in Dubai Emirate. Globally, this species is distributed from the Sinai Peninsula of Egypt through much of the Arabian Peninsula to Iran and southern Pakistan (Cassola 2016a).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
Habitat details as listed in assessment
Predominantly crepuscular and nocturnal and prefers all kinds of rocky habitats (Harrison and Bates 1991). Found on boulder-strewn slopes and rocky terrain where it lives in crevices among boulders (Cunningham 2008) and in wadi beds in Wadi Wurayah (Judas 2016). In a community structure study of Jebel Al Jais in Ras Al Khaimah Emirate, the species was recorded at elevations ranging from 450-“1,650 m, was most abundant in the wadi area around 450 m, and its abundance declined with increasing altitude (Melville and Chaber 2016). It was trapped at around 180 m asl on he outlying hill of Jebel Nazwa (Qarn Nazwa) in 2018 (J. Judas pers. comm. 2018). This species is omnivorous (Melville and Chaber 2016). There is evidence from trapping surveys that the Arabian Spiny Mouse is more susceptible than other small mammal species to disturbance and fragmentation (B. Howarth pers. comm. 2018).
Threats and conservation measures listed
Threats listed in assessment
Overgazing, quarrying, road construction and other development activities in the mountains result in habitat loss and degradation and increased fragmentation. Species in the mountains may also be affected indirectly by falling water tables due to over-abstraction and reduced precipitation. An increase in numbers of feral cats and Red Foxes may also pose a threat to all small mammals.
History
The backcasted 1996 assessment for this species is Near Threatened (almost meets a threatened listing under criterion B1ab(iii)) which matches the listing given by Hornby (1996).
Publication
Mallon, D., Hilton-Taylor, C., Allen, D., & Harding, K. (2019). UAE National Red List of Mammals: Marine and Terrestrial. A report to the Ministry of Climate Change and Environment, United Arab Emirates (p. 41). IUCN Global Species Programme. https://bit.ly/2RdZCQR
Assessment ID
329885
Taxon name
Physeter macrocephalus
Linnaeus, 1758
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Physeter macrocephalus
Linnaeus, 1758
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
cetartiodactyla
Family
physeteridae
Genus
Physeter
Species
macrocephalus
Species authority
Linnaeus, 1758
Taxonomic notes and synonyms listed
Although Physeter catodon is still occasionally used in the literature, P. macrocephalus is recommended (Rice 1989). Both names are listed on the same page of the original description by Linnaeus (1758), and priority is unclear. However, P. macrocephalus is preferable because it is used much more frequently, and this will support nomenclatural stability.
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Data deficient
Abbreviated status
DD
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
In UAE waters, this species is known from only a few strandings and sightings. No information on population size and trends or on threats is available, so it is assessed as Data Deficient. No regional adjustment is made to the Data Deficient assessment.
Assessment details
Year assessed
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
There are no records from the Gulf, but this species is recorded off the east coast (Baldwin et al. 1999, Baldwin 2005). Two dead Sperm Whales have been recorded at Fujairah in recent years; one washed ashore on a beach adjacent to Fujairah Port in 2012 and one was found by <a href=""https://www.thenational.ae/uae/environment/20-metre-sperm-whale-found-dead-on-fujairah-coast-1.8318"">Fujairah Port authorities</a> on 15th June 2017, floating at sea approximately one nautical mile from the port breakwater which was recovered, and buried to allow decomposition. There was a stranding in 2016 at Khor Kalba (Sharjah). There are sightings and a video in 2015 and 2016 off Dibba, northern tip of the eastern Arabian Peninsula. Live females and juveniles have been seen off Fujairah (Baldwin 2005), suggesting that they may breed in the region, and there has been one observation of a mature bull seen with a female pod (<a href=""http://fujairahwhales.com/sperm-whale/"">Fujairah Whales</a>). The species has a large global range in nearly all marine regions, from the equator to high latitudes, but it is generally found in deeper water (Taylor et al. 2008).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
Habitat details as listed in assessment
Found in deep water on continental shelves. Groups may include as many as 20-50 individuals, but single animals or small pods of 2-6 are more common (Baldwin et al. 1999). Individuals observed 30 nautical miles due east of Fujairah in 1995 were positioned directly above the edge of the continental shelf, where the water depth suddenly changes from less than 600 m to well over 1,000 m. This is ideal habitat for feeding sperm whales, which may remain submerged for over an hour and can dive to a depth of 3,000 m in pursuit of giant squid and other prey (Baldwin 2005).
Threats and conservation measures listed
Threats listed in assessment
The main threats to cetaceans in UAE waters include: incidental mortality in trawl, drift and anchored gill nets, depletion of prey populations (due in part to commercial overfishing); ship and boat strikes, disturbance due to underwater noise (including that from vessel traffic, drilling, piling, military operations and seismic activity related to offshore oil and gas exploration). Evidence for human-caused mortality of sperm whales, including those caused by ship-strike and fisheries interactions, have been described from an assessment of a limited number of strandings in Oman and the UAE (Gray et al. 2017). Other potential threats in the region include sound pollution from oil exploration activities (e.g., seismic and multi-beam echo sounder surveys), and military sonar (Baldwin 2003). A lack of information (e.g. population size and trend, the location of critical habitats, and feeding ecology) hinders the development of appropriate conservation actions, but this should be used as an excuse for inaction.
History
The backcasted 1996 assessment for this species is Data Deficient which matches the listing given by Hornby (1996).
Publication
Mallon, D., Hilton-Taylor, C., Allen, D., & Harding, K. (2019). UAE National Red List of Mammals: Marine and Terrestrial. A report to the Ministry of Climate Change and Environment, United Arab Emirates (p. 41). IUCN Global Species Programme. https://bit.ly/2RdZCQR
Assessment ID
329883
Taxon name
Tursiops aduncus
(Ehrenberg, 1833)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Tursiops aduncus
(Ehrenberg, 1833)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
cetartiodactyla
Family
delphinidae
Genus
Tursiops
Species
aduncus
Species authority
(Ehrenberg, 1833)
Taxonomic notes and synonyms listed
The Indo-Pacific Bottlenose Dolphin (Tursiops aduncus) has been recognized as a different species from the more widely distributed Common Bottlenose Dolphin (Tursiops truncatus) since the late 1990's (Rice, 1998). Indo-Pacific Bottlenose Dolphins are distinct from Common Bottlenose Dolphins based on concordance among genetic, osteology, coloration and external morphology data (Wang et al. 1999, 2000a,b). No Indo-Pacific Bottlenose Dolphin subspecies are currently recognised by the Society for Marine Mammalogy's Committee on Taxonomy (2018). However, a recent re-assessment of Tursiops taxonomy worldwide (IWC 2019) and extensive genetic studies (Moura et al. 2013, Amaral et al. 2016, Gray et al. 2018) identified 4 or 5 different lineages (Africa, Pakistan, Bay of Bengal, China and Australia), including the recently described ""T. australis"" (Charlton-Robb et al., 2011) that may eventually be recognized as a subspecies. There is considerable population structure throughout the range of the species and multiple studies of morphology (Hale et al., 2000, Kemper 2004, Charlton-Robb et al., 2011) and genetics (Natoli et al. 2004, Särnblad et al. 2011, Charlton-Robb et al. 2011, Amaral et al. 2016) indicate that the taxonomic status for a number of populations in different regions should be re-evaluated.
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
A2bc
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
Preen (2004) reported a 71% decline in small species of dolphins in the Arabian Gulf from 1986 to 1999, which included this species. There is no information available on decline rates in the individual species, so based on the assumption that they all declined equally it appears reasonable to infer a population reduction of &gt;50% for Tursiops aduncus over the past three generations (63 years). Even accounting for animals off the east coast, the species, therefore, qualifies for assessment as Endangered (EN) under criterion A2bc. The reduction was due to a combination of pressures including declining habitat quality because of increasing coastal development, bycatch, collision with boats and declines in fish stocks. The decline is continuing but it is not possible to say if it is at the same rate. There is unlikely to be a significant rescue effect as it is considered likely that the population across the whole of the Gulf area has declined.
Assessment details
Year assessed
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
In UAE waters, this species occurs in both the Arabian Gulf and the Gulf of Oman. The Indo-Pacific Bottlenose Dolphin (as well as the Indo-Pacific Humpback Dolphin) is the species most likely to be seen close to shore in Abu Dhabi and Dubai (Baldwin 2005). Globally, this species has a discontinuous distribution in the warm temperate to tropical Indo-Pacific, from South Africa in the west, as far east as the Solomon Islands and the southern half of Japan and southeast Australia (Hammond et al. 2012c).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
Habitat details as listed in assessment
Typically, bottlenose dolphins are found in groups of 5-“35 individuals in the UAE, although much larger groups can occur. They are fast, powerful swimmers, often riding the bow wave of boats. As their reputation in aquaria attests, they are inquisitive and capable of spectacular aerial acrobatics. Indo-Pacific Bottlenose Dolphins have been observed feeding over sand, seagrass and reefs in the Arabian Gulf (Baldwin 2005).
Threats and conservation measures listed
Threats listed in assessment
The main threats to cetaceans in UAE waters include: incidental mortality in trawl, drift and anchored gill nets, depletion of prey populations (due in part to commercial overfishing); ship and boat strikes, disturbance due to underwater noise (including that from vessel traffic, drilling, piling, military operations and seismic activity related to offshore oil and gas exploration). Inshore and shallow-water species are further potentially threatened by entanglement in abandoned fishing gear, coastal development including port and harbour construction, dredging, land reclamation, residential and tourist development, and pollution (especially hydrocarbons). During surveys by EAD, a large number of dolphins were observed with scars that were attributed to propeller cuts, indicating that vessel strike is a major threat to dolphin populations in Abu Dhabi waters (EAD 2015). A UAE Fisheries Resource Assessment Survey in 2002 found that fish stocks in the Gulf had declined by 60%. A lack of information (e.g. population size and trend, the location of critical habitats, and feeding ecology) hinders the development of appropriate conservation actions, but this should be used as an excuse for inaction.
History
The backcasted 1996 assessment for this species is Endangered under the same criterion as the current assessment. Hornby (1996) assessed the status of both Tursiops species under a combined taxonomic concept using the name ""T. truncatus"" and listed it as Near Threatened, however, it appears he was not aware of the 71% decline in the species from 1986 to 1999 as reported by Preen (2004).
Publication
Mallon, D., Hilton-Taylor, C., Allen, D., & Harding, K. (2019). UAE National Red List of Mammals: Marine and Terrestrial. A report to the Ministry of Climate Change and Environment, United Arab Emirates (p. 41). IUCN Global Species Programme. https://bit.ly/2RdZCQR
Assessment ID
329882
Taxon name
Mellivora capensis
(Schreber, 1776)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Mellivora capensis
(Schreber, 1776)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
carnivora
Family
mustelidae
Genus
Mellivora
Species
capensis
Species authority
(Schreber, 1776)
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Data deficient
Abbreviated status
DD
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The population status and distribution of the Honey Badger in the UAE is uncertain. It is known from a small number of historical and recent records from southern and western Abu Dhabi Emirate and recent sightings from low relief areas within the Hajar Mountains. It is thus assessed as Data Deficient. The species may have a marginal occurrence in the UAE, with a global range that extends from northwestern Africa to Central Asia. No regional adjustment is made to the Data Deficient assessment.
Assessment details
Year assessed
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The status and distribution of the Honey Badger in the UAE is uncertain. Tracks were reported in the late 1940s between Liwa and the Sabkha Matti (Thesiger 1949). There have been two more recent reports of tracks: in 1991 between Liwa and Umm al Zummoul and 1992 in the Baynoonah area (Duckworth 1996, Drew and Tourenq 2005, Aspinall et al. 2005). The first definitive record in the UAE was in August 2005, when three specimens, two live and one dead, were recorded near Ruwais in western Abu Dhabi (Aspinall et al. 2005). This record appears to have been overlooked by Mallon and Budd (2011) and others. Tracks were seen in 2010 in Baynoonah, western Abu Dhabi. There are two reports from the Northern Emirates (G. Feulner, pers. comm. 2018): In the late 1990s or early 2000s, Jaap Wensvoort, then manager of a reserve north-east of Hatta, reported a sighting from an elevated viewpoint, of a 'waddling, black-and-white animal crossing the plain below'. The only reasonable candidate seems to be the Honey Badger. In 2016, a Dubai naturalist and photographer observed a Honey Badger feeding not long after dark beside the trash area at an informal picnic site above a dam on the western mountain front. The Honey Badger has an extensive global range in most of sub-Saharan Africa from South Africa north to southern Morocco and southwestern Algeria, and through Arabia, Iran and western Asia and Central Asia (Do Linh San et al. 2016).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
Habitat details as listed in assessment
Baynoonah, where the specimens were recorded, is in open desert. In the Northern Emirates, two of three known reports are associated with human activity. No other information on the ecology of the species in UAE is available. Honey Badgers occur in a wide range of habitats in Arabia, including sand and gravel plains, wadis, mountains up to 2,200 m (Harrison and Bates 1991, Mallon and Budd 2011) but in UAE they have only been confirmed from the desert
Threats and conservation measures listed
Threats listed in assessment
Subject to generalised persecution of carnivores. No information specific to UAE is available.
History
Whilst Hornby (1996) listed this species as Critically Endangered, at that time the species' occurrence in the UAE was unconfirmed as only tracks had been reported in the 1940s and once in 1996. Since that time there has been a record of three specimens which confirms its presence, but nothing more is known. The backcasted 1996 assessment for this species is, therefore, Data Deficient.
Publication
Mallon, D., Hilton-Taylor, C., Allen, D., & Harding, K. (2019). UAE National Red List of Mammals: Marine and Terrestrial. A report to the Ministry of Climate Change and Environment, United Arab Emirates (p. 41). IUCN Global Species Programme. https://bit.ly/2RdZCQR
Assessment ID
329881
Taxon name
Ichneumia albicauda
(G. Cuvier, 1829)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Ichneumia albicauda
(G. Cuvier, 1829)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
carnivora
Family
herpestidae
Genus
Ichneumia
Species
albicauda
Species authority
(G. Cuvier, 1829)
Taxonomic notes and synonyms listed
This species is occasionally mistaken with Meller's Mongoose (Rhynchogale melleri), which also sometimes has a white tail. However, the White-tailed Mongoose is usually larger, and its body appears black, rather than brown (Skinner and Chimimba 2005). Further confusion in identification is sometimes created by the fact that Ichneumia albicauda individuals with black tails have been recorded in several areas of the African distribution range (A. Page pers. comm. 2014, C. Wright pers. comm. 2014). Only one subspecies has been listed, from southern Africa, I. a. grandis (Thomas 1890), but the nominate form has a wide distribution across much of the rest of Africa (Meester et al. 1986).
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
D
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The White-tailed Mongoose occurs in the north of the UAE mainly in the mountains but is also known from some sites in the plains. The lack of recent sightings makes it difficult to determine the population size, but it is estimated that there are fewer than 250 mature individuals and hence it is assessed as Endangered (EN) under criterion D. Any potential rescue effect is thought to be insignificant.
Assessment details
Year assessed
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The White-tailed Mongoose occurs in the north of the UAE mainly in the mountains but also known from some sites in the plains (Jongbloed et al. 2001, Aspinall et al. 2005, Fernandes 2011). It has been recorded from Wadi Shawkah and other sites in Ras Al Khaimah; Wadi Siji in Fujairah; it was seen in Wadi Wurayah in the late 1990s (J. Budd pers. comm. 2018), but has not been recorded there in recent camera trap surveys; and Wadi Helo and Wadi Hefiyah in Sharjah. Outside the mountains, it has been recorded at Al Ain, Al Dhaid (where two were caught in 2015) and Masafi. It was listed as Extinct in the Wild in Abu Dhabi (Drew and Tourenq 2005). The species is widespread in sub-Saharan Africa from Senegal and Gambia to the Horn of Africa, and then southwards to South Africa (Do Linh San 2015). In the Arabian Peninsula, it occurs in Oman. Yemen and Saudi Arabia, in addition to UAE (Mallon and Budd 2011). The species occurs in the Hajar Mountains in Oman (Harrison and Bates 1991).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
Habitat details as listed in assessment
Prefers mountain wadis and is normally found near permanent water; it avoids open desert. It is mainly nocturnal and preys on reptiles, small mammals, insects, birds and their eggs and carrion, and has adapted to living in close proximity to humans (Aspinall et al. 2005).
Threats and conservation measures listed
Threats listed in assessment
May be subject to persecution by poultry farmers. Habitat in the Hajar Mountains is being lost, degraded and fragmented by quarrying, road building, and residential and tourism development. As the presence of the species appears to be linked to permanent water, the disappearance of freshwater habitats and decreasing water tables in wadis due to over-abstraction might be a potential threat. Red Foxes are increasing their range in the mountains and may be a competitor or predator.
History
The population is suspected to have declined due to habitat loss and degradation, fragmentation, and competition with increasing populations of Vulpes vulpes. Whilst it was assessed as Endangered by Hornby (1996), we consider it likely that there were &gt;250 individuals in 1996, and so back-cast the category to Vulnerable (VU D1).
Publication
Mallon, D., Hilton-Taylor, C., Allen, D., & Harding, K. (2019). UAE National Red List of Mammals: Marine and Terrestrial. A report to the Ministry of Climate Change and Environment, United Arab Emirates (p. 41). IUCN Global Species Programme. https://bit.ly/2RdZCQR
Assessment ID
329880
Taxon name
Lepus capensis
Linnaeus, 1758
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Lepus capensis
Linnaeus, 1758
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
lagomorpha
Family
leporidae
Genus
Lepus
Species
capensis
Species authority
Linnaeus, 1758
Taxonomic notes and synonyms listed
The entire taxonomy of Lepus capensis throughout its range is unclear. Taxonomic review of the species is urgently needed; otherwise, it is possible that some forms may go extinct before they are formally identified. Hoffmann and Smith (2005) restricted L. capensis to the South African distribution, citing no evidence of gene flow between the southern and northern ranges. A list of synonyms is provided based on four geographic locations (South Africa, East Africa, Arabia and Near East, and northwest Africa), which are informal subdivisions of L. capensis sensu lato. The authors suggested that these four groups might represent distinct species. In the Near East and Arabia L. c. arabicus; in South Africa L. c. capensis; L. c. aquilo, L. c. carpi, L. c. granti; East Africa L. c. aegyptius, L. c. hawkeri, L. c. isabellinus, L. c. sinaiticus; and L. c. atlanticus, L. c. schulmbergeri, L. c. whitakeri in northwest Africa (Hoffmann and Smith 2005, Schai-Braun and Hackländer 2018). According to Harrison and Bates (1991) there are eight subspecies in Arabia: L. c. syriacus (Syria, Lebanon, northern Israel); L. c. sinaiticus (southern Israel, Sinai); L. c. connori (east of the Euphrates in Iraq); L. c. arabicus (western Iraq, Kuwait, Saudi Arabia, Yemen); L. c. cheesmani (Saudi Arabia, Qatar, UAE, Yemen, Oman); L. c. omanensis (UAE, Oman); L. c. atallahi (Bahrain, Qatar?); L. c. jefferyi (Masirah Island, Oman). The taxonomic status of L. c. jefferyi needs clarification, as it may represent a good species. Hares present in Qatar also require taxonomic investigation. The taxonomic position of the Sardinian Hare is unresolved. Hoffmann and Smith (2005) include the Sardinian Hare as one of the unassigned synonyms of L. mediterraneus Wagner, 1841 or typicus Hilzheimer, 1906, in L. granatensis. Analysis of the mtCR-1 sequence indicated that Sardinian Hares form a monophyletic clade with North African Hares (Scandura et al. 2007). A genetic and morphometric analysis supports the hypothesis that the Sardinian Hare was introduced from North Africa (Canu et al. 2012). A phylogenetic analysis of mtCR-1 sequences from Tunisian and Egyptian Hares characterized them as monophyletic and separate from L. capensis (Ben Slimen et al. 2006). However, a study of the nuclear gene pool of L. capensis, L. europaeus and the North African Hare indicated that the North African Hare as well as L. europaeus belong to L. capensis (Ben Slimen et al. 2005), supporting Petter's (1959, 1961) hypothesis of the inclusion of L. europaeus in capensis. Ben Slimen et al. (2008a) suggest that in a case such as the genus Lepus, where evolution is ""rapid and to some extent reticulate"", species designation based solely on mtDNA is misleading without examination of the nuclear gene pool. Ben Slimen et al. (2008a) has shown that genetic differentiation between L. capensis and L. europaeus could be attributed to geographic distance rather than divergence. They speculate that gene flow may be occurring in the Near East where distributions meet resulting in the potential for intergraded populations. However, Ben Slimen et al. (2008b) propose that ""a combined phylogenetic, phylogeographic, and population genetic approach, based on various nuclear and mitochondrial markers and including other biological characters, such as phenotypic and morphometric data,"" is needed for conclusive evidence of a single species complex. A recent study looking at a partial transferrin nuclear gene and phylogenetic relationship of hares in Tunisia showed shared ancestral polymorphism between North African and Chinese hares (Awadi et al. 2016). It also concluded that the Tunisian Hare is well differentiated from hares considered belonging to brown hares L. europaeus from central Europe (Awadi et al. 2016). In light of this continuing uncertainty regarding the taxonomic status of the Sardinian and North African Hares, both will remain included in capensis and L. europaeus retains its taxonomic status as a distinct species. Many treatments indicate that the range of L. capensis extends into China, Mongolia and Russia; however, recognition of L. tibetanus and L. tolai as distinct species removes consideration of L. capensis as occurring in this region (Hoffmann and Smith 2005).
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Least concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The Cape or Arabian Hare is widely distributed across the UAE except in the mountains. It is currently assessed as Least Concern because it remains widespread and relatively common inside protected areas, and releases from captive breeding programmes are ongoing. Outside protected areas, habitat loss and degradation due to overgrazing is widespread and continuing so the species could be approaching the thresholds for listing as Near Threatened and regular monitoring is required. No regional adjustment is made to the Least Concern assessment.
Assessment details
Year assessed
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Cape or Arabian Hare is widely distributed across the UAE except in the mountains and has been introduced onto some islands such as Al Yasat and Abu al Abyadh (Aspinall et al. 2005, Drew and Tourenq 2005). Globally, it is distributed across the whole of the Arabian Peninsula, extending through Iran east into India. It also ranges extensively in Africa outside the central rainforest zone (Drew et al. 2008).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
Habitat details as listed in assessment
Occurs in coastal flats, gravel plains and sand dunes. Hares make forms at the base of shrubs, sometimes making use of abandoned fox or Uromastyx burrows (Drew 2004). Hare pellets occurred in higher numbers in areas free from domestic grazing than in areas with high grazing pressure or anthropogenic impact (Drew 2000). Hares have home ranges of 11-“30 hectares (0.11-“0.3 km<sup>2</sup>). In summer they are more likely to be found on the fringe of sand dunes where there are shrubs such as Haloxylon salicornicum beneath which they can excavate burrows. In winter they are found most commonly on vegetated plains or flat sandsheets. The movement from dunes in summer to flat areas in winter may be related to mate selection and reproduction (Drew 2004).
Threats and conservation measures listed
Threats listed in assessment
The expansion of human settlement into the deserts and the impact of camel grazing on the vegetation have had a significant effect on the hare's habitat in UAE, outside protected areas. Many plains formerly covered by succulent vegetation are now totally barren due to over-grazing and, possibly, over-extraction of groundwater. Moreover, many forestry plantations have large numbers of feral cats and Red Fox Vulpes vulpes which predate hares (Aspinall et al. 2005, Drew and Tourenq 2005). Releases of individuals imported from southern and Central Asia have been implicated in deaths of native hares due to the introduction of disease (suspected to be rabbit haemorrhagic disease) (Drew 2004). Releases of non-native hares may also pose a risk to the genetic integrity of the indigenous population.
History
The backcasted 1996 assessment for this species is Least Concern which matches the listing given by Hornby (1996).
Publication
Mallon, D., Hilton-Taylor, C., Allen, D., & Harding, K. (2019). UAE National Red List of Mammals: Marine and Terrestrial. A report to the Ministry of Climate Change and Environment, United Arab Emirates (p. 41). IUCN Global Species Programme. https://bit.ly/2RdZCQR