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Assessment ID
329878
Taxon name
Paraechinus hypomelas
(Brandt, 1836)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Paraechinus hypomelas
(Brandt, 1836)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
eulipotyphla
Family
erinaceidae
Genus
Paraechinus
Species
hypomelas
Species authority
(Brandt, 1836)
Taxonomic notes and synonyms listed
Treated by some authors under the genus Hemiechinus.
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
This species is restricted to the eastern UAE, but is listed as Least Concern because the species is common in the mountains, no major threats have been reported, and there is no indication of a decline. There is no need for a regional adjustment of the category.
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
Restricted to the eastern UAE, this species is most common in rocky areas but avoids the highest elevations. Regularly recorded around Al Ain, where it overlaps with the Desert Hedgehog (Paraechinus aethiopicus), and Jebel Hafeet (Abu Dhabi); also recorded from Dhaid (Sharjah), Hatta (Dubai), Wadi Bih (Ra's al-Khaimah), and Dibba on the east coast and the hills west of Khor Fakkan (Fujairah) (Aspinall et al. 2005). The species is widely distributed from the Arabian Peninsula and Iran, through southern Central Asia to Afghanistan and Pakistan (Bhattacharyya 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
In southeast Arabia, Brandt's Hedgehog prefers mountainous areas and may be a montane relic species (Harrison and Bates 1991).
Threats and conservation measures listed
Threats listed in assessment
No major threats are known at present. In the longer term, falling water tables in mountain wadis due to over-abstraction and a drier climate may result in a deterioration in habitat quality.
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
Assessment ID
329877
Taxon name
Paraechinus aethiopicus
(Ehrenberg, 1832)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Paraechinus aethiopicus
(Ehrenberg, 1832)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
eulipotyphla
Family
erinaceidae
Genus
Paraechinus
Species
aethiopicus
Species authority
(Ehrenberg, 1832)
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
This is a widespread and common species in the UAE and, although declining in some areas due to loss of habitat, it is still common, hence listed as Least Concern. There is no need for a regional adjustment of the category.
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 is the most widespread species of hedgehog in the UAE, occurring in a wide range of habitats except mobile dunes. It has been introduced to several islands in Abu Dhabi (Aspinall et al. 2005, Drew and Tourenq 2005). The species occurs in most of the Arabian Peninsula and is also widely distributed in North and Northeast Africa from Morocco and Mauritania to Sudan and Ethiopia, as well as the Middle East (Hutterer 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
Recorded in gardens, cultivation, oases, vegetated wadis, plains and deserts (Aspinall et al. 2005). Nocturnal and becomes less active during the hottest summer months.
Threats and conservation measures listed
Threats listed in assessment
The species may be impacted by the loss of habitat through urban development, though residential development including gardens may increase available habitat. It is frequently seen as a road casualty.
History
Whilst Hornby (1996) assessed the species as Near Threatened, we consider it likely that the appropriate category would have been Least Concern in 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
329858
Taxon name
Rousettus aegyptiacus
(E. Geoffroy, 1810)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Rousettus aegyptiacus
(E. Geoffroy, 1810)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
chiroptera
Family
pteropodidae
Genus
Rousettus
Species
aegyptiacus
Species authority
(E. Geoffroy, 1810)
Taxonomic notes and synonyms listed
The taxonomic relationship with Rousettus leschenaultii requires further review. Two geographically isolated subspecies of R. aegyptiacus occur in sub-Saharan Africa (Monadjem et al. 2010). Both subspecies occur in the southern African region: unicolor (Gray, 1870) in Angola and leachii (A. Smith, 1829) in the rest of the region (Monadjem et al. 2010). Additional subspecies: princeps is endemic to Principe Island in the Gulf of Guinea and tomensis is endemic to Sao Tome (Korine 2016).
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 species appears to be moderately common in eastern parts of the UAE, and may be increasing as a result of the expansion of fruit tree cultivation. It is assessed as Least Concern because it is fairly widespread, with an expanding range and population, due to the planting of fruit trees, and no major threats are known. 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
There are two records from Abu Dhabi city and many more from the northern emirates and the Hajar Mountains and adjacent areas (Judas et al. 2018), and this species may well occur in intervening areas where suitable habitat such as fruit plantations exists. Recorded sites include Al Ain, the Fujairah coast, Sharjah, and Hatta (Dubai), on farms outside the protected area. Globally, the species is distributed across most of Africa, through the Middle East to Turkey, Iran and Pakistan (Korine 2016). It is quite widely distributed in the Arabian Peninsula (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
Roosts in caves and rock crevices and feeds in date plantations, orchards and gardens (Judas et al. 2018).
Threats and conservation measures listed
Threats listed in assessment
No major threats are known, but there are some cases of poisoning.
History
Whilst the species was assessed as Vulnerable for the UAE (Hornby 1996), we consider that the species would have also been Least Concern in 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
329857
Taxon name
Vulpes vulpes
(Linnaeus, 1758)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Vulpes vulpes
(Linnaeus, 1758)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
carnivora
Family
canidae
Genus
Vulpes
Species
vulpes
Species authority
(Linnaeus, 1758)
Taxonomic notes and synonyms listed
A recent extensive global phylogeny of Red Foxes that included ~1,000 samples from across the species' range found that Red Foxes originated in the Middle East, then radiated out, and that Red Foxes in North America are genetically distinct and probably merit recognition as a distinct species (Vulpes fulva) (Statham et al. 2014).
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 Red Fox is found throughout the UAE in a variety of habitats. It is assessed as Least Concern because it is widespread and common and apparently increasing. 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 Red Fox is found throughout the UAE in a variety of habitats, from arid, rocky mountains to sandy desert, coastal plains and small offshore islands. This is a highly adaptable species that has benefited from the expansion of human habitation, farms, irrigated plantations to extend its distribution into the deserts of the interior (Aspinall et al. 2005, Drew and Tourenq 2005). Over 25 Red Foxes were disturbed in 1992 while feeding on the refuse tip at the Shah oilfield, south of Liwa, deep in the desert (Hellyer 1993). The Red Fox has a very extensive global range covering the entire northern hemisphere, and it has been introduced elsewhere (Hoffmann and Sillero-Zubiri 2016). It is common across the Arabian Peninsula (Mallon and Budd 2011).
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
An adaptable species occupying a wide range of habitats and taking advantage of the expansion of human settlements. Opportunistic and omnivorous, Red Foxes will eat almost anything they can catch or find, including small mammals, birds, insects, carrion, plants and fruits (Aspinall et al. 2005).
Threats and conservation measures listed
Threats listed in assessment
Subject to shooting and trapping by farmers, game bird breeders and others.
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
Assessment ID
329856
Taxon name
Vulpes rueppellii
(Schinz, 1825)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Vulpes rueppellii
(Schinz, 1825)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
carnivora
Family
canidae
Genus
Vulpes
Species
rueppellii
Species authority
(Schinz, 1825)
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
Critically endangered
Abbreviated status
CR
Qualifying criteria (if given)
C2a(i)
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
Within the UAE, this species is considered to be confined mainly to the remoter desert regions of Abu Dhabi Emirate. It is assessed as Critically Endangered under criterion C2a(i) because there are estimated to be less than 250 mature individuals, there is an inferred and projected decline and no subpopulation contains >50 mature individuals. The potential rescue effect is considered negligible.
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 considered to be confined mainly to the remoter desert regions of Abu Dhabi Emirate and its range is believed to have contracted as roads and development extend further into the desert, facilitating colonisation by, and competition with, Vulpes vulpes (Jongbloed et al. 2001, Aspinall et al. 2005). There are only 52 records since 1992 on the EAD database. The only confirmed recent site in Abu Dhabi is Al Dhafra (Murdoch et al. 2007). It has not been recorded at Umm Al Zumoul or Liwa. In Dubai, it has not been recorded at Al Marmoom. There were no records from Dubai Desert Conservation Reserve until a pair was released; recent camera trap photos may relate to descendants of these animals or to a colonising animal. There are no records from the desert of Sharjah Emirate. Globally this species is widespread in desert and semi-desert regions of North Africa (north of 17'°N) from Morocco and Mauritania to Egypt, extending south to Somalia and through the Middle East to Pakistan (Mallon et al. 2015). It is thinly distributed across the Arabian Peninsula and has also been recorded from Oman, Saudi Arabia, and Yemen (Harrison and Bates 1991, Mallon and Budd 2011).
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
Inhabits arid steppe, sandy, stony and rocky deserts (Larivière and Seddon 2001). Crepuscular and nocturnal, spending the day underground in breeding and resting dens either dug themselves or enlarged burrows of Spiny-tailed Lizards (dhab) Uromastyx aegyptia (Olferman and Hendrichs 2006). They are agile and climb trees, fences and rocks (Larivière and Seddon 2001). Small mammals and birds formed 85-90% of the diet based on analysis of almost 3,000 scats (Olferman and Hendrichs 2006).
Threats and conservation measures listed
Threats listed in assessment
Overgrazing, especially by camels, has caused extensive habitat degradation outside protected areas which likely impacts on small mammal and other prey populations. Road construction and development are extending into the desert, facilitating colonisation by, and competition with, Vulpes vulpes. Generalised persecution (trapping, poisoning) of carnivores, loss and fragmentation of desert habitat, grazing pressure, agricultural development, and off-road driving in sand dune areas are the main threats in the region and in parts of UAE at least, it has been displaced around settlements by V. vulpes (Mallon and Budd 2011).
History
There are no recent records from the deserts of the northern Emirates. Records from Abu Dhabi are very scarce, even within protected areas, and there is only one record since 2007. Desert habitats have been degraded, destroyed and fragmented by overgrazing, development and road-building which has facilitated the expansion of Red Foxes, which outcompete this species, into desert environments. The population is suspected to have now declined to below 250 mature individuals. The backcasted 1996 assessment for this species is Vulnerable under criterion D1 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
329855
Taxon name
Vulpes cana
Blanford, 1877
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Vulpes cana
Blanford, 1877
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
carnivora
Family
canidae
Genus
Vulpes
Species
cana
Species authority
Blanford, 1877
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
Vulnerable
Abbreviated status
VU
Qualifying criteria (if given)
D1
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This species is now restricted in the UAE to upland areas within the Hajar Mountains and Jebel Hafeet. It is assessed as Vulnerable under criterion D1 because the population size is estimated to be less than 1,000 and may well be close to 250 based on the information from recent sightings. The assessment is not adjusted as there is unlikely to be any rescue effect from populations in adjoining countries.
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 species was first confirmed in the UAE by Stuart and Stuart (1995). Subsequent research using camera traps and live traps has shown it to be common throughout the Hajar Mountains up to the Oman border on the Musandam Peninsula and on Jebel Hafeet, where a skull was found in 2009 (Llewellyn-Smith 2000, Aspinall et al. 2005, Mallon and Budd 2011). Locations include Wadi Bih, Wadi Shawka, Wadi Shuwayhah, Wadi Ziqt (Cunningham and Howarth 2002). It has been recently camera trapped in Wadi Wurayah and is quite often camera trapped in Ras Al Khaimah. However, in the mountains of Sharjah Emirate and at Hatta in Dubai there have been no records of the species in the last few years, only Red Fox, although access to the wadis in Hatta area has been restricted in recent years, hindering possible surveys. It was described as common at levels on Jebel Hafeet by Drew (2004) but There have been no records from Jebel Hafeet for the last few years where Red Foxes, feral dogs and feral cats now dominate the area. This is most likely due to transformation of the habitat due primarily to release of waste water and subsequent changes to the vegetation on the mountain, and with increased human presence, as well as residential and amenity development at the base. Globally, Blanford's Fox occurs in the mountains around the rim of the Arabian Peninsula including Sinai (Egypt), Iran, Turkmenistan and Pakistan. There is a single record from Egypt west of the Suez Canal (Hoffmann and Sillero-Zubiri 2015).
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
Restricted to the mountains and avoids the foothills and plains inhabited by Vulpes vulpes. Nocturnal. Extremely agile and an exceptional jumper, this species preys on invertebrates, reptiles, small mammals and fruit. Very little is known about their social structure. In captivity, two to four young are normally born between February and April after a gestation period of approximately 50 days (Aspinall et al. 2005). One analysis of faeces (n=4) showed that the diet of this species includes a variety of insects (Mantodea, Orthoptera, Coleoptera, Diptera, Hymenoptera) and spiders, a feather, unidentified bone remains, a gerbil incisor, fur, a reptile pelvis and snail remains (Cunningham and Howarth 2002). The diet also includes fruit seeds and plant material, selection of species depending on what is available locally (Cunningham and Howarth 2002). This study also noted the difference in tail tip colour: out of ten individuals caught in the UAE, seven had black tail tips and two white tips.
Threats and conservation measures listed
Threats listed in assessment
Habitat in the Hajar Mountains is being lost, degraded and fragmented by quarrying, road building, pipelines, and residential and tourism development. On Jebel Hafeet, the available habitat has been reduced by development along the lower reaches (Drew and Tourenq 2005) and this factor now also affects the upper slopes. Blanford's Fox may be affected by generalised predator persecution but is unlikely to be targeted specifically. It may also be outcompeted by the larger and more adaptable Vulpes vulpes taking advantage of expanding developments in the mountains.
History
The backcasted 1996 assessment for this species is Vulnerable under criterion D1 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
329854
Taxon name
Vespertilio murinus
Linnaeus, 1758
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Vespertilio murinus
Linnaeus, 1758
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
chiroptera
Family
vespertilionidae
Genus
Vespertilio
Species
murinus
Species authority
Linnaeus, 1758
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 is only known from a single record in the UAE, a dead individual found in 2014. The species may be treated as marginal to the UAE, but as bats are in general very under-recorded it is considered 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 only record of this species in the UAE, and also the first record for the Arabian Peninsula, is a specimen found dead on 13 May 2014 at the Breeding Centre for Endangered Arabian Wildlife, Sharjah, and identified on molecular (cytochrome b gene) and morphological characters (Monadjem et al. 2016). Widely distributed across the whole northern Palaearctic, from Western Europe to Siberia and northern China and the Pacific coast and south to northern Iran, Central Asia, Afghanistan and northern Pakistan. The nearest colonies to UAE are in western Iran and Afghanistan (Coroiu 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
Across its global range, the Particoloured Bat occupies a wide range of open and wooded habitats (Coroiu 2016). It is a migratory species (Monadjem et al. 2016).
Threats and conservation measures listed
Threats listed in assessment
No information available.
History
This species was not listed by Hornby (1996) for the UAE Red List of mammals, but based on current knowledge the backcasted 1996 assessment for this species is 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
329853
Taxon name
Tursiops truncatus
(Montagu, 1821)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Tursiops truncatus
(Montagu, 1821)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
cetartiodactyla
Family
delphinidae
Genus
Tursiops
Species
truncatus
Species authority
(Montagu, 1821)
Taxonomic notes and synonyms listed
All Bottlenose Dolphins around the world were previously recognized as Tursiops truncatus, but currently, the genus is considered to be composed of two species: T. truncatus (Common Bottlenose Dolphin) and T. aduncus (the smaller Indo-Pacific Bottlenose Dolphin) (Wang et al. 1999, 2000a,b). The Common Bottlenose Dolphin has a worldwide distribution in tropical and temperate latitudes but exhibits a strong ability to adapt to local conditions, a complex social structure and strong site fidelity which results in considerable habitat partitioning throughout its range. This, in turn, has created strong population differentiation accompanied, in some cases, by marked morphological differentiation. The taxonomy of Bottlenose Dolphins is confused due to this geographical variation, and it is very possible that additional species will be recognized in the future. Three subspecies are currently recognized by the Society for Marine Mammalogy's Committee on Taxonomy (2017) and a recent re-assessment of Tursiops taxonomy worldwide conducted by the International Whaling Commission confirmed their validity (IWC 2018). These subspecies are the Black Sea Bottlenose Dolphin (T. t. ponticus Barabash-Nikiforov, 1940) which differs morphologically and genetically from other forms including those in the nearby Mediterranean Sea (Barabash-Nikiforov 1960, Geptner et al. 1976, Natoli et al. 2005, Viaud-Martinez et al. 2008). The Lahille Bottlenose Dolphin (T. t. gephyreus) (Lahille, 1908), a larger form in the coastal waters of the western South Atlantic Ocean, is morphologically and genetically different from the offshore population in eastern South America (Costa et al. 2015, 2016; Fruet et al. 2011, 2015). The third subspecies is the nominate subspecies that includes the remaining Common Bottlenose Dolphins worldwide (T. t. truncatus (Montagu, 1821)). In the western North Atlantic, two forms, offshore and coastal, are distinguishable on the basis of morphology and ecological markers (Mead and Potter 1995) and have fixed genetic differences (Le Duc and Curry 1997, Hoelzel et al. 1998, Kingston et al. 2009, Rosel et al. 2009, Van Waerebeek et al. 2017a) and according to the recent IWC review the coastal population should be recognized as at least a different subspecies.
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
There is currently no information available on the population size and trends, hence it is assessed as Data Deficient (DD). Until recently this species was thought to be more widespread in the UAE waters, but it is now known that the species found in the Gulf should be treated as Tursiops aduncus (many specimens from the Gulf were misidentified as T. truncatus). There is potential for a rescue effect, but as the species is listed as DD, that regional assessment cannot be 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
The species occurs in the Gulf of Oman, but is apparently absent from the Arabian Gulf, reflecting a preference for deep, offshore water. Globally, this species is distributed through all tropical and temperate inshore, coastal, shelf, and oceanic waters (Hammond et al. 2012d).
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, Common 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. Common Bottlenose Dolphins have been observed feeding in deep water off the east coast (500-“2,000 m) (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). 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. 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; as it is a different concept that assessment cannot be used.
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
329851
Taxon name
Taphozous perforatus
E. Geoffroy, 1818
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Taphozous perforatus
E. Geoffroy, 1818
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
chiroptera
Family
emballonuridae
Genus
Taphozous
Species
perforatus
Species authority
E. Geoffroy, 1818
Taxonomic notes and synonyms listed
Meester et al. (1986) recognised three subspecies, including the nominate subspecies (Taphozous perforatus perforatus) from Egypt (where this species was initially described), T. p. sudani Thomas, 1915 from Sudan, and T. p. haedinus Thomas, 1915 from Kenya. However, it remains uncertain how the geographically isolated southern African population (named T. p. rhodesiae, and described from the Shashi-Limpopo confluence; Harrison 1964) is related to these subspecies (Monadjem et al. 2010). T. p. rhodesiae was originally recognised as a subspecies of T. sudani (T. sudani australis), which was previously identified as a distinct species from T. perforatus (ACR 2015).
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 bat is assessed as Data Deficient because the species was first recorded in 2018 from one site in the Hajar Mountains. 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 bat was first recorded in the UAE in early 2018 when 11 individuals were caught in a cave in Wadi Al Hab, Fujairah (Jomat et al. 2018). There are also records of the species from several localities in adjacent parts of the Hajar Mountains in Oman (Harrison and Bates 1991). The species may previously have been confused with Taphozous nudiventris. The species occurs widely throughout northern and sub-Saharan Africa, the Arabian Peninsula and Asia, east to the Indian subcontinent (Monadjem et al. 2017e).
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 only UAE record was in a cave in the Hajar Mountains. The species inhabits caves, crevices and old buildings (Harrison and Bates 1991).
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 by falling water tables due to over-abstraction and reduced precipitation.
History
The backcasted 1996 assessment for this species is 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
329850
Taxon name
Taphozous nudiventris
Cretzschmar, 1830
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Taphozous nudiventris
Cretzschmar, 1830
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
chiroptera
Family
emballonuridae
Genus
Taphozous
Species
nudiventris
Species authority
Cretzschmar, 1830
Taxonomic notes and synonyms listed
Simmons (2005) assigns four subspecies to Taphozous nudiventris: T. n. kachhensis Dobson, 1872; T. n. magnus Wettstein 1913; T. n. nudaster Thomas, 1915; and T. n. zayidi Harrison, 1955. The enigmatic taxon T. n. serratus Heuglin, 1877 has been variously referred to either Taphozous nudiventris (e.g., Allen 1939, Koopman 1993) or Scotophilus leucogaster (e.g., Allen 1939, Koopman 1975), although it might not represent either of these species. See Felten (1962), Hayman and Hill (1971), Bates and Harrison (1991, 1997) and Bates et al. (1994) for further information on this taxon.
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
Vulnerable
Abbreviated status
VU
Qualifying criteria (if given)
D1
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
Within the UAE, this species is known from a colony at Qarn Nazwa (Dubai) and further records from Al Ain (Sharjah) and Das Island (Abu Dhabi) in the Gulf. The resident population of this bat is assessed as Vulnerable under criterion D1 because the population in the country was estimated to number 150 in 2009, but the numbers are likely to be higher than that now, but almost certainly less than the threshold of 1,000 mature individuals. The visiting population on Das Island (which is a different subspecies) could be assessed separately, however, that is not done here as it is considered to be too marginal (only a tiny portion of the global population of the subspecies occurs within the UAE).It is not known how much movement there is of this species across the region, hence it is not possible to determine if there is any rescue effect from populations in adjoining countries.
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 is a colony at Qarn Nazwa (Dubai; Gardner 2009) and further records from Al Ain, Sharjah, and Das Island in the Gulf (Judas et al. 2018). The subspecies recorded on Das Island is Taphozous nudiventris magnus, a winter migrant from Iraq, Bahrain or further north; the subspecies occurring in the rest of the UAE is T. n. zayidi (Judas et al. 2018). The global range extends across North Africa from Morocco to Egypt and south to northern Tanzania, the Middle East, southern Turkey, and east to the Indian subcontinent (Monadjem et al. 2017a).
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
Roosts in crevices, cliffs and buildings (Harrison and Bates 1991). The colony on Qarn Nazwa roosts in rock crevices. Migrants from farther north in the Gulf have been recorded on Das Island.
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 invertebrates, the main prey base.
History
Although Hornby (1996) assessed the species as Data Deficient, it is considered that the species also qualified for listing as Vulnerable (VU) under criterion D1 in 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