Assessment ID
329849
Taxon name
Steno bredanensis
Uploaded by
National Red List Database
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
329848
Taxon name
Stenella longirostris
Uploaded by
National Red List Database
Scientific name
Stenella longirostris
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
cetartiodactyla
Family
delphinidae
Genus
Stenella
Species
longirostris
Taxonomic notes and synonyms listed
Recent genetic work indicates that the genus Stenella is paraphyletic and it is likely that the Delphininae will be restructured in the coming years (LeDuc et al. 1999, Perrin et al. 2013). Four subspecies of Spinner Dolphins are currently recognized: S. l. longirostris (Gray's Spinner Dolphin), S. l. orientalis (Eastern Spinner Dolphin), S. l. centroamericana (Central American Spinner Dolphin) and S. l. roseiventris (Dwarf Spinner Dolphin) (Perrin 1990, Perrin et al. 1999). There is a zone of hydridisation between Gray's Spinner and the Eastern Spinner where an intermediate form called the White-bellied Spinner occurs (Andrews et al. 2013). Smaller individuals in Arabian waters (Red Sea and Arabian Gulf) (Van Waerebeek et al. 1999) and morphologically different animals in West Africa may represent as yet undescribed subspecies (Cadenat 1959, Jefferson et al. 1997). Several studies have demonstrated significant meta-population genetic structure, especially where relatively insular dolphin communities are strongly associated with island resting habitat such as in the Hawaiian Archipelago (Andrews et al. 2013) and in the South Pacific (Oremus et al. 2007).
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
Assessed as
Data deficient
Abbreviated status
DD
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
In UAE waters this species is found in both Gulf waters and off the east coast. There is insufficient information available on population size or trends of this species in UAE waters, hence it is assessed as Data Deficient. No regional adjustment is made to the Data Deficient assessment.
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.
URL (link) of redlist assessment or publication
https://www.moccae.gov.ae/assets/download/b352eff1/UNRL%20of%20Mammals%20-%20Report%202019.pdf.aspx?view=true
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Occurrence in the Arabian Gulf was first confirmed from skulls found on UAE offshore islands in 1995; it has since been sighted 20 km off the city of Dubai and its range continues to at least 100 km west of Abu Dhabi and also stretches eastwards around the Musandam Peninsula into the Indian Ocean (Baldwin 2005). There are no confirmed inshore sightings from the Gulf, where the water is shallower. Spinner Dolphins are also known from deep water east of Fujairah Port and offshore from Kalba. Globally, the species ranges through tropical and subtropical zones in both hemispheres approximately between 40'°N and 40'°S (Bearzi et al. 2012, Braulik and Reeves 2018).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
Spinner Dolphins live well offshore in deep water, where they feed on small fish. Spinner Dolphins occur both in the open ocean and in inshore waters associated with islands or banks (Braulik and Reeves 2018).
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). 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
329847
Taxon name
Stenella coeruleoalba
Uploaded by
National Red List Database
Scientific name
Stenella coeruleoalba
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
cetartiodactyla
Family
delphinidae
Genus
Stenella
Species
coeruleoalba
Taxonomic notes and synonyms listed
Recent genetic work suggests that the genus Stenella is paraphyletic, and it is likely that the Delphininae will be restructured in coming years (LeDuc et al. 1999, Perrin et al. 2013). Morphological and genetic studies strongly suggest that the Mediterranean and eastern North Atlantic Striped Dolphin populations are isolated from each other, with little or no gene flow across the Strait of Gibraltar (Calzada and Aguilar 1995, García-Martínez et al. 1995, Archer 1997, Gaspari 2004). No subspecies are recognized.
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
Assessed as
Data deficient
Abbreviated status
DD
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species is known only from a few recent sightings off Fujairah on the east coast of the UAE. No further information is available on population size or trends, and there are also no data on the impact of threats to the species, hence it is assessed as Data Deficient. No regional adjustment is made to the Data Deficient assessment.
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.
URL (link) of redlist assessment or publication
https://www.moccae.gov.ae/assets/download/b352eff1/UNRL%20of%20Mammals%20-%20Report%202019.pdf.aspx?view=true
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Fishermen from Fujairah claimed to encounter this species (Baldwin 2005), however, the first confirmed records for the UAE were in waters off the east coast in April 2017 during surveys by the Fujairah Whale and Dolphin Research Project. Mostly considered very rare in the Arabian region, this species has since been observed off Fujairah on several occasions, including in mixed groups with <a href=""http://fujairahwhales.com/striped-dolphin/"">Spinner and Pantropical Spotted Dolphins</a>. The species has not been observed along the Gulf coast. Globally, this is a widely-distributed species, found in tropical and warm-temperate waters of the Atlantic, Pacific, and Indian oceans, as well as many adjacent seas (Hammond et al. 2008b).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
The species is found in deep offshore waters but are seen close to shore where deep water approaches the coast, as found off the east coast of the UAE.
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). 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.
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
329846
Taxon name
Stenella attenuata
Uploaded by
National Red List Database
Scientific name
Stenella attenuata
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
cetartiodactyla
Family
delphinidae
Genus
Stenella
Species
attenuata
Taxonomic notes and synonyms listed
The genus Stenella is paraphyletic, and it is likely that the Delphininae will be restructured in the coming years (LeDuc et al. 1999, Perrin et al. 2013). Two subspecies are recognized: S. attenuata attenuata in oceanic tropical waters worldwide, and S. a. graffmani in the coastal waters of the eastern tropical Pacific (ETP) (Jefferson et al. 2015, Perrin 2018).
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
Assessed as
Data deficient
Abbreviated status
DD
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species is known only from a few recent sightings off the coast of Fujairah and an old skull record from the Gulf. No further information is available on population size or trends, and there are also no data on any threats to the species, hence it is assessed as Data Deficient. No regional adjustment is made to the Data Deficient assessment.
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.
URL (link) of redlist assessment or publication
https://www.moccae.gov.ae/assets/download/b352eff1/UNRL%20of%20Mammals%20-%20Report%202019.pdf.aspx?view=true
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The only UAE records of this species are a skull collected on the Gulf coast in 1973 (Baldwin 2005) and individuals observed off the coast of Fujairah during a survey by the <a href=""http://fujairahwhales.com/pantropical-spotted-dolphin/"">Fujairah Whale and Dolphin Research Project</a> in 2017. Baldwin et al. (1999) collated references to this species from the Arabian Gulf, the Gulf of Oman, the Arabian Sea, Gulf of Aden, and the Red Sea. Globally it is found in all oceans between about 40'°N and 40'°S, although it is much more abundant in the lower-latitude parts of its range (Hammond et al. 2012a, Kiszka and Braulik 2018).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
Occurs in offshore waters where it hunts in the thermocline for small pelagic fish. Found in groups from 10 to 300 (Baldwin et al. 1999).
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). 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
329845
Taxon name
Rhinopoma muscatellum
Uploaded by
National Red List Database
Scientific name
Rhinopoma muscatellum
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
chiroptera
Family
rhinopomatidae
Genus
Rhinopoma
Species
muscatellum
Taxonomic notes and synonyms listed
Earlier the taxa muscatellum Thomas, 1903 and seianum Thomas, 1913 were treated as subspecies of Rhinopoma hardwickii Gray, 1831 (Ellerman and Morrison-Scott 1951). Individuals from Afghanistan, Iran and Pakistan are considered as R. muscatellum seianum based on morphometric and molecular phylogenetic analysis (Benda et al. 2012). The nominotypic subspecies is now restricted to the Arabian Peninsula (Benda and Gaisler 2015).
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
Assessed as
Least concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The species appears to be restricted to eastern parts of the UAE, in and around the Hajar Mountains and to Qarn Nazwa. It is assessed as Least Concern because it is widespread, relatively common, and there are no major threats. No regional adjustment is made to the Least Concern assessment.
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.
URL (link) of redlist assessment or publication
https://www.moccae.gov.ae/assets/download/b352eff1/UNRL%20of%20Mammals%20-%20Report%202019.pdf.aspx?view=true
Endemic to region
Not assigned
Taxon distribution as listed in assessment
All records are from the east of UAE, in and around the Hajar Mountains and at the rocky outcrop of Qarn Nazwa. Recorded localities include Al Ain and Jebel Hafeet (Abu Dhabi); Qarn Nazwa (Dubai); Dibba and Wadi Wurayah National Park (N.P.) (Fujairah); Al Khatt, Rams (Ras Al Khaimah); Khor Kalba (Sharjah) (Judas et al. 2018). During a bat survey of the Hajar Mountains in early 2018, a total of 36 individuals were caught at four sites (Jomat et al. 2018). In Arabia, this species is restricted to Oman and UAE (Harrison and Bates 1991). Globally, its range extends to Iran, Afghanistan and Pakistan (Harrison and Bates 1991, Molur et al. 2008).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
Roosts in caves and rock crevices.
Threats listed in assessment
No major threats are known. 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
Whilst Hornby (1996) assessed the species as Data Deficient, we consider that Least Concern is probably the appropriate category 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
329843
Taxon name
Pseudorca crassidens
Uploaded by
National Red List Database
Scientific name
Pseudorca crassidens
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
cetartiodactyla
Family
delphinidae
Genus
Pseudorca
Species
crassidens
Taxonomic notes and synonyms listed
No subspecies of False Killer Whale (Pseudorca crassidens) are currently recognized. However, there is evidence of geographic variability in skull morphology and life history (Kitchener et al. 1990, Ferreira et al. 2014). Based on genetics there is substantial population structure, both between and within-ocean basins, and even within a single archipelago (Martien et al. 2014). This species has been intensively studied only in Hawaii (Baird 2016) and more recently in New Zealand (Zaeschmar 2014). In Hawaii, three subpopulations have been identified based on a combination of genetic studies (Martien et al. 2014), satellite tagging (Baird et al. 2010, 2012, 2014, Bradford et al. 2014a), and analyses of photo-identification data (Baird et al. 2008, Baird 2016). These include two partially overlapping insular populations, one around the main Hawaiian Islands, and one in the northwestern Hawaiian Islands, as well as a partially overlapping pelagic population that ranges throughout and beyond the U.S. Exclusive Economic Zone (EEZ) around the Hawaiian Archipelago. In New Zealand, based on high resighting rates of photo-identified individuals and a relatively small number of individuals documented, it is likely that this represents a distinct subpopulation (Zaeschmar 2014). While the number of subpopulations world-wide is unknown, this is due primarily to incomplete sampling in most of the range. Based on the evidence from Hawaii, subpopulation structure likely exists throughout their range.
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
Assessed as
Data deficient
Abbreviated status
DD
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
On the Gulf coast, the species is known from a small number of records of skeletal remains and strandings, whilst it has been reported off the east coast but not in recent surveys. There is insufficient information available on population size or trends of this species in UAE waters, hence it is assessed as Data Deficient. No regional adjustment is made to the Data Deficient assessment.
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.
URL (link) of redlist assessment or publication
https://www.moccae.gov.ae/assets/download/b352eff1/UNRL%20of%20Mammals%20-%20Report%202019.pdf.aspx?view=true
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Skeletal remains of this species have been found in the Gulf on island beaches in western Abu Dhabi (Baldwin 2005). There was a stranding reported from Sir Bani Yas in 2013/2014 and a possible sighting in Dubai in 2015. It is reported off the east coast but was not recorded on surveys in 2017-2018 by the Fujairah Whale and Dolphin Project. There was a sighting of an injured individual in 2012 off Dibba (Musandam). Globally it is found in tropical to warm temperate zones, generally in relatively deep, offshore waters of all three major oceans (Taylor et al. 2008, Baird 2018).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
Found in deep water on continental shelves where it feeds on fish species such as tuna. Observed in groups of 1-“300 (Baldwin et al. 1999).
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). 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
Hornby (1966) considered the species to be Near Threatened, however, we consider DD to be the appropriate backcasted assessment for this species 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
329842
Taxon name
Pipistrellus kuhlii
Uploaded by
National Red List Database
Scientific name
Pipistrellus kuhlii
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
chiroptera
Family
vespertilionidae
Genus
Pipistrellus
Species
kuhlii
Taxonomic notes and synonyms listed
Simmons (2005) considers sub-Saharan African and Canary Island populations to belong to a different species, P. hesperidus, but the taxonomic validity of that taxon, as well its relation with the African P. deserti needs further research. The species in Yemen requires taxonomic clarification (D. Kock pers. comm. 2005).Pipistrellus deserti is considered a junior synonym of P. kuhlii following Benda et al. (2014).
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
Assessed as
Least concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species is assessed as Least Concern because it is widespread in the UAE and common, and there are no major threats. No regional adjustment is made to the Least Concern assessment.
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.
URL (link) of redlist assessment or publication
https://www.moccae.gov.ae/assets/download/b352eff1/UNRL%20of%20Mammals%20-%20Report%202019.pdf.aspx?view=true
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This is the most widespread and one of the most abundant species of bat in the UAE (Judas et al. 2018). There are records from many localities, including coastal areas and islands of all emirates. The species is widespread in Arabia and was described as 'abundant' by Harrison and Bates (1991). Globally, the species is widespread in Africa and Europe, the Arabian Peninsula, Middle East and the Caucasus to Kazakhstan, Pakistan, and India (Juste and Paunovic 2016).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
Roosts colonially. Observed packed together in cracks between coral blocks used to build houses in Sharjah and also in falaj tunnels at Al Ain (Harrison and Bates 1991), and may make use of caves and crevices in between rocks. It occurs in a wide range of desert habitats and mountain wadis.
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 species was considered Data Deficient by Hornby (1996), however, we consider it likely that the species would also have qualified as 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
329841
Taxon name
Panthera pardus
Uploaded by
National Red List Database
Scientific name
Panthera pardus
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
carnivora
Family
felidae
Genus
Panthera
Species
pardus
Taxonomic notes and synonyms listed
According to genetic analyses, nine subspecies are recognized, with all continental African Leopards attributable to the nominate form, P. p. pardus (Miththapala et al. 1996, Uphyrkina et al. 2001).
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
Assessed as
Regionally extinct
Abbreviated status
RE
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
There are a number of records of Leopard in the mountains of the northern UAE and it is once likely to have occurred widely there. However, the species is assessed as Regionally Extinct because there have been no confirmed records since 1994 and there is no convincing evidence to show that the species still occurs in UAE. There is no rescue effect because there are believed to be no leopards left in Musandam or the northern Hajar Mountains of Oman.
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.
URL (link) of redlist assessment or publication
https://www.moccae.gov.ae/assets/download/b352eff1/UNRL%20of%20Mammals%20-%20Report%202019.pdf.aspx?view=true
Endemic to region
Not assigned
Taxon distribution as listed in assessment
There are a number of records of Leopard in the mountains of the northern UAE and it is once likely to have occurred widely there. Thesiger (1949) wrote that a Leopard visited Jebel Hafeet ...some years ago. There is a report of a Leopard shot in Masafi, east of Sharjah, in 1962 (Harrison 1968) and another report from Qalidda Pass (Harrison 1971). Hellyer (1993) said there had been nine reports in the previous 30 years. These included one wounded on Jebel Hafeet in 1976, which later died in Al Ain Zoo; a male shot in Ras al Khaimah in July 1986; a female and two young adults in the same Emirate in December 1986, and the capture of one Leopard near Masafi in February 1991. A leopard was shot in the upper part of Wadi Zibat, a tributary of Wadi Bih with permanent water, in November 1992 and its skull retrieved, and another was shot in the same locality in May 1993 (Hellyer 1993). A Leopard was killed in the Al Wa'eeb area of Musandam in 1994 and another was seen there in August 1994 (Hellyer 1994). Since then there have been a few reports of Leopard tracks in the mountains, including at Hatta, but none of these has been confirmed. Summaries of Leopard status in UAE are provided in Aspinall et al. (2005) and Edmonds et al. (2006). There is no convincing evidence to indicate that the species is still present in UAE. Reports from the Omani sector of the Musandam Peninsula continued through the 1970s, 1980s, and 1990s, including eight killed in 1980, but with no confirmed reports since 1997 it appears that the species no longer occurs in the Hajar Mountains of Oman (Spalton et al. 2006). Leopards are widely distributed across Africa and Asia, but they have been extirpated from large portions of their historic range (Stein et al. 2016). Populations across the Arabian Peninsula are at critically low levels (Mallon and Budd 2011).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
All UAE records are from mountains and wadis in the Hajar range.
Threats listed in assessment
Persecution (shooting, trapping and poisoning) as well as reduction in the prey base (due to hunting and competition with increasing numbers of livestock), development of wadis, limited access to water, and fragmentation are considered to be the main causes of the decline of the species in UAE (Edmonds et al. 2006). The reports in the 1990s coincided with abundant rainfall during that decade, which was not the case in the 2000s, and drought may have hastened the disappearance of the species from the UAE (G. Feulner, pers. comm. 2018).
History
There have been no confirmed records since 1994 and there is no convincing evidence to show that the species still occurs in UAE. Hornby (1996) assessed the species as Critically Endangered, perhaps on the assumption that some animals may persist. The backcasted 1996 assessment for this species is Critically Endangered (CR D).
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
329840
Taxon name
Oryx leucoryx
Uploaded by
National Red List Database
Scientific name
Oryx leucoryx
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
cetartiodactyla
Family
bovidae
Genus
Oryx
Species
leucoryx
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
Assessed as
Vulnerable
Abbreviated status
VU
Qualifying criteria (if given)
D1
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The Arabian Oryx was reportedly once common in parts of western UAE, but declined due to uncontrolled hunting and it became Extinct in the Wild in the UAE sometime in the 1960s or early 1970s. The species has recovered as a result of intensive conservation efforts. There are now currently an estimated 1,480-1,630 mature individuals in the UAE at the four main reintroduction sites. The lower estimate would qualify listing the species as Near Threatened under criterion D1. However, these estimates may be high as a result of supplementary feeding. Assuming conservatively that 20% of the oryx would survive for ten years if the feeding ceased (as required by the Red List Guidelines) the number of mature individuals surviving would be around 300-360 (the number surviving might be higher but would probably be less than 1,000 mature individuals); therefore the Arabian Oryx is assessed as Vulnerable under criterion D1. There is no rescue effect because the nearest subpopulation in Saudi Arabia is small (c.100) and the international border is now completely fenced.
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.
URL (link) of redlist assessment or publication
https://www.moccae.gov.ae/assets/download/b352eff1/UNRL%20of%20Mammals%20-%20Report%202019.pdf.aspx?view=true
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Arabian Oryx was reportedly common in the Manasir area of western UAE, ranging into the Rub Al Khali (Philby 1933) but declined due to uncontrolled hunting and it became Extinct in the Wild in the UAE sometime in the 1960s or early 1970s. It has since been reintroduced to several sites: the Arabian Oryx Protected Area at Umm al Zumoul in southeast Abu Dhabi; Qasr Al Sarab Protected Area, which lies adjacent to the AOPA to the west; Dubai Desert Conservation Reserve (DDCR), and Al Marmoom Conservation Area and adjacent desert in Dubai. Oryx are also present in government and private collections, some of which are extensive, and managed under a range of different conditions. The Arabian Oryx formerly occurred through most of the Arabian Peninsula, north to Kuwait and Iraq. The species' range had already contracted by the early years of the 20th century and the decline accelerated thereafter. Before 1920, oryx distribution was separated into areas over 1,000 km apart: a northern subpopulation in and around the Nafud (Saudi Arabia), and a larger southern subpopulation in the Rub Al Khali and the plains of central-southern Oman. Oryx disappeared from the north in the 1950s. In the south, their range steadily decreased due to hunting, and by the 1960s Oryx were restricted to parts of central and southern Oman. The last wild individuals were probably shot in 1972 on the Jiddat al Harasis, Oman. Arabian Oryx have been reintroduced to several sites across the Arabian Peninsula in addition to the sites in the United Arab Emirates. There is an introduced subpopulation on Hawar Island, Bahrain and large semi-managed subpopulations at several sites in Qatar, UAE and Saudi Arabia (Harrison and Bates 1991, IUCN SSC Antelope Specialist Group 2017c).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
The species inhabits sand and gravel deserts and avoids mountains. Arabian Oryx feed at night during the summer months, resting under shady trees during the heat of the day, while in winter they feed during the daytime, sheltering from cool desert winds at night (Aspinall et al. 2005). In high ambient temperatures, their body temperature increases, excess heat being lost later by radiation during the cooler night hours. Oryx meet almost all their water needs by eating plants with high water content and by feeding at a time when water from fog and dew is at its maximum. Oryx rarely run but can walk long distances at a steady pace, covering up to 50 km in a night (Aspinall et al. 2005).
Threats listed in assessment
Uncontrolled hunting from motor vehicles is believed to be the principal cause of the disappearance of the oryx from the wild. Released populations and those in private collections are now safe from this threat, but the security of animals outside these sites cannot be guaranteed. Drought and overgrazing have reduced habitat quality in places and limited the choice of potential release sites. Fenced sites are also subject to the risk of density-dependent mortality especially in cases of prolonged drought: e.g. 560 oryx died in such conditions in Mahazat as Sayd reserve in west-central Saudi Arabia over the period 1999-2008 (Islam et al. 2010).
History
Hornby (1996) assessed the species Extinct in the Wild and this status is used as the backcasted assessment for the species 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
329839
Taxon name
Orcinus orca
Uploaded by
National Red List Database
Scientific name
Orcinus orca
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
cetartiodactyla
Family
delphinidae
Genus
Orcinus
Species
orca
Taxonomic notes and synonyms listed
This taxonomic unit is treated as a single species even though there is extensive and growing evidence that it is, in fact, a complex of multiple forms with morphological, genetic, ecological, and behavioural differences that merit subspecies if not also species designations. At the time of writing (June 2017), the Committee on Taxonomy of the Society for Marine Mammalogy (<a href=""https://www.marinemammalscience.org/species-information/list-marine-mammal-species-subspecies/"">www.marinemammalscience.org/species-information/list-marine-mammal-species-subspecies</a>), which is generally regarded as the authority for marine mammal taxonomy, recognized a single killer whale species, Orcinus orca (Linnaeus, 1758), and two unnamed subspecies in the eastern North Pacific, the ENP resident killer whale (O. o. un-named subsp.) and the ENP transient killer whale (O. o. un-named subsp.) also known as Bigg's killer whale. The Committee noted, however, Other forms of killer whales in the North Pacific, North Atlantic and Antarctic [Southern] Ocean may warrant recognition as separate subspecies or even species, but the taxonomy has not yet been fully clarified or agreed (Morin et al. 2010; Foote et al. 2009, 2013). One population (a distinct population segment) of the ENP resident subspecies (the southern resident population) was listed as Endangered under the Canadian Species at Risk Act in 2003 and the U.S. Endangered Species Act in 2005.
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
Assessed as
Data deficient
Abbreviated status
DD
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species is known from both the Gulf and east coasts where it is probably a regular visitor rather than a resident. However, there is insufficient information available on population size or trends of this species in UAE waters, hence it is assessed as Data Deficient. No regional adjustment is made to the Data Deficient assessment.
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.
URL (link) of redlist assessment or publication
https://www.moccae.gov.ae/assets/download/b352eff1/UNRL%20of%20Mammals%20-%20Report%202019.pdf.aspx?view=true
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Killer Whales are found off the east coast of the UAE but they also enter the Gulf. There are confirmed sightings from near Mubarraz, west of Abu Dhabi in March 2000 and off Jebel Ali in November 2000 (Baldwin 2005). One individual sighted off Abu Dhabi (UAE) in 2008 was resighted in Sri Lanka in 2015 (G.L. Gemmell pers. comm. 2018), suggesting that Killer Whales in this region migrate long distances. There were two records off Abu Dhabi in 2008, including a stranding and a sighting in 2011. It is seen about once a year in Dubai waters, including one off Palm Jumeira in 2014, and at Ra's Kharab in 2015. There were records off Umm al Qawain in 2011 and 2017. Killer Whales were sighted at least twice in the Gulf in 2017, in both Iranian and UAE waters, and once in 2018 in Iran (H. Moshiri pers. comm. 2018). It is probably a regular visitor rather than a resident species in UAE waters. The Killer Whale is the most cosmopolitan of all cetaceans and may occur in virtually any marine habitat but is most common in cold-water areas of high marine productivity, particularly at higher latitudes and near-shore (Reeves et al. 2017).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
Generally lives in the open ocean. Prey in the UAE may include other cetaceans as well as turtles, seabirds and cold-blooded species such as fish and squid (Baldwin 2005).
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). 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
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