United Arab Emirates

Official name
United Arab Emirates
ISO alpha-2 code
AE
ISO alpha-3 code
ARE
ISO numeric-3 code
784
Continent
Asia

Suncus etruscus | UAE National Red List of Mammals: Marine and Terrestrial

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Incomplete
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
The areas where specimens have been obtained consist of sandy and gravel desert with scattered trees and bushes, and irrigated farmland. Little is known about this species in the Arabian region (Harrison and Bates 1991).
Taxon
Taxa
Suncus etruscus | (Savi, 1822)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Mammals
Assessed taxon level
Species
Taxon distribution as listed in assessment
First recorded in UAE in August 2000 during live-trapping at the Breeding Centre for Endangered Arabian Wildlife, Sharjah (Aspinall et al. 2005) and has been recorded there again since then. There is an observation from Abu Dhabi of a Southern Grey Shrike Lanius meridionalis feeding on this species (Drew and Tourenq 2005) and it has been recorded at Al Wathba Wetland Reserve (Soorae et al. 2014). Photographs of two recent sightings at Green Mubazzarah, at the base of Jebel Hafeet, have been published on the <a href=""http://www.uaebirding.com/photos-mammals.html"">UAE Birding website</a>. The species may also have been caught in Al Ain. The species is difficult to live-trap due to its very low weight and it is likely to occur more widely in the UAE. The species is widespread from southern Europe and North Africa through the Near East and Arabian Peninsula to Central Asia, and South and Southeast Asia, including the island of Borneo (Aulagnier et al. 2017).
Assessed status
Asessment status in full
Data deficient
Assessment status abreviation
DD
About the assessment
Assessment year
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species is assessed as Data Deficient for the UAE because this is a poorly known species, with only very few, widely scattered records. No regional adjustment is made to the Data Deficient assessment.
Criteria system
Criteria system specifics
IUCN v3.1
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
There is no information available on threats to this species.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
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 has to be Data Deficient.
Verified entry
Off

Otonycteris hemprichii | UAE National Red List of Mammals: Marine and Terrestrial

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
The UAE records are from a mountain wadi. It also occurs in open desert areas and roosts in rock crevices and sometimes in buildings (Harrison and Bates 1991).
Taxon
Taxa
Otonycteris hemprichii | Peters, 1859
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Mammals
Assessed taxon level
Species
Taxon distribution as listed in assessment
The only records for UAE consist of skulls retrieved in 1972 from raptor pellets found in a cave in Ras Al Khaimah (Harrison 1977). It may occur more widely in UAE, especially the Hajar Mountains (Harrison and Bates 1991, Jomat et al. 2018, Judas et al. 2018). The species is distributed across the desert zone from Morocco to northwest India and it is widespread in the Arabian Peninsula.
Assessed status
Asessment status in full
Data deficient
Assessment status abreviation
DD
About the assessment
Assessment year
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species is assessed as Data Deficient because only a single old record is known, from Ras Al Khaimah. The species may well occur elsewhere in the country, however, it is also possible that the specimen remains may not have originated from within the UAE. No regional adjustment is made to the Data Deficient assessment.
Criteria system
Criteria system specifics
IUCN v3.1
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
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.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
The backcasted 1996 assessment for this species is Data Deficient which matches the listing given by Hornby (1996).
Verified entry
Off

Eptesicus bottae | UAE National Red List of Mammals: Marine and Terrestrial

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
The single UAE record was from a mountain wadi. Across its global range, this is a versatile species that occupies a wide range of habitats (Harrison and Bates 1991); it is usually a crevice-dwelling species, inhabiting buildings, ruins (including tombs), and natural rock crevices throughout the year. This bat feeds usually on ants and moths but also on beetles (Whitaker and KarataÅŸ 2009).
Taxon
Taxa
Eptesicus bottae | (Peters, 1869)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Mammals
Assessed taxon level
Species
Taxonomic Notes
In previous Red List assessments, Eptesicus anatolicus and E. ognevi were included in E. bottae (Juste et al. 2013, Artyushin et al. 2018). Those are now considered separately and have their own assessments.
Taxon distribution as listed in assessment
This species was first recorded in the UAE by Jomat et al. (2018) who caught two individuals over a pool in Wadi Wurayah, Fujairah. There may be other records from echolocation calls but these have not yet been confirmed. In Oman, the species is recorded from Wadi Sahtan in the Hajar Mountains (Harrison and Bates 1991). This is a Palaearctic species, occurring from the eastern Mediterranean to Iran, the southern Caucasus and Central Asia to India, northwestern China and possibly Mongolia (Aulagnier et al. 2008).
Assessed status
Asessment status in full
Data deficient
Assessment status abreviation
DD
About the assessment
Assessment year
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species is newly recorded for the UAE following survey work in early 2018, when the species was found over a pool in Wadi Wurayah, Fujairah. The species is assessed as Data Deficient because there is only one confirmed record and the status of the species in the country has not been established. No regional adjustment is made to the Data Deficient assessment.
Criteria system
Criteria system specifics
IUCN v3.1
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
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.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
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.
Verified entry
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Aetomylaeus nichofii | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
Yes
Habitat
Habitat details as listed in assessment
The Banded Eagle Ray is a demersal species in continental shelf inshore waters to at least 115 m depth (Last and Stevens 2009). It reaches a maximum size of 72 cm disc width (DW) with males maturing at 39-42 cm DW (Last et al. 2016). Size at maturity for females is unknown, but pregnant females have been recorded in the UAE at 54.8 cm DW (R.W. Jabado pers. comm. 06/05/2017). Females are viviparous with litters of up to four young with a size at birth of 17 cm DW (Compagno and Last 1999, Last and Stevens 2009). Nothing else is known of this species' biology. Generation length estimated at 10 years based on the generation length of the Bat Ray (Myliobatis californicus) (14.5 years) (Martin and Cailliet 1988). However, it is noted that the Bat Ray is a considerably larger species (reaching 180 cm DW) than the Banded Eagle Ray.
Taxon
Taxa
Aetomylaeus nichofii | (Bloch & Schneider, 1801)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
Aetomylaeus caerulofasciatus has recently been described as distinct from the wider-ranging Indo-West Pacific A. nichofii (White et al. 2015).
Taxon distribution as listed in assessment
The Banded Eagle Ray occurs throughout UAE waters (Randall 1995, Carpenter 1997, Hellyer and Aspinall 2005, Environment Agency Abu Dhabi unpublished data). Globally, it is widespread in the Indo-West Pacific (Spaet and Berumen 2015, Last et al. 2016).
Assessed status
Asessment status in full
Vulnerable
Assessment status abreviation
VU
Assessment status criteria
A2cd
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
The Banded Eagle Ray occurs throughout UAE inshore waters, and is common. This species is not targeted or valued in markets of the UAE and trawling has been banned there since 1980. It is caught as bycatch in inshore gill net fisheries. It is under extremely intense and increasing demersal fishing pressure in much of the Arabian Sea region, and declines have been detected in Pakistan, India and the Red Sea. The loss and degradation of coastal habitats in the Gulf is a significant concern. It is especially susceptible to exploitation (target and bycatch) in many largely unregulated gill net, longline and trawl fisheries that operate within its range outside and surrounding UAE waters. Some management measures are now in place in the Arabian Sea region, although domestic fisheries are likely to continue. Though data specifically from the UAE are not available, individuals in the UAE are a component of a larger, interconnected and migratory population that occurs broadly in the north-western Indian Ocean. It is inferred that declines reported in the Arabian Sea region are representative of its status in the UAE. Based on recorded levels of exploitation and decline in habitat quality, it is suspected to have declined by at least 30% over the past three generation lengths, or about 45 years. It is listed as Vulnerable A2cd.
Criteria system
Criteria system specifics
IUCN v3.1
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
This species is impacted by fisheries in the UAE and forms a relatively large portion of all landed batoids. It is impacted by bycatch fisheries that are active elsewhere in its range as well. Marine habitats in the Gulf are experiencing high levels of disturbance and quickly deteriorating due to major impacts from development activities (including dredging and reclamation), desalination plants, industrial activities, habitat destruction through the removal of shallow productive areas and major shipping lanes (Sheppard et al. 2010).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Allosorus acrosticus | UAE National Red List of Vascular Plants

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
In the Ru'us al-Jibal, it is found in the shelter of boulders to c. 1,900 m asl (Feulner 2011).
Taxon
Taxa
Allosorus acrosticus | (Balb.) Christenh.
Taxonomic Group
Plants
Taxonomic Group Level 2
Ferns and Allies
Assessed taxon level
Species
Taxonomic Notes
This is an allotetraploid species derived from the hybridisation between A. pteridioides and A. persicus.
Taxon distribution as listed in assessment
In the UAE, this species is common in the Ru'us al-Jibal to c. 1,900 m asl (Feulner 2011, Rothfels et al. 2012). There are scattered records to the south from the Hajar Mountains, including a record from the upper part of Wadi Siji in the Wadi Wurayah National Park buffer zone (WWNP; Feulner 2016). D. Aplin (pers. comm. 2020) found a new southern record for the species in the UAE, from Ra's al Khaimah, west of Al Hayl. Rothfels et al. (2012) record numerous records of the species from adjacent parts of the Musandam Peninsula. Globally, this is a mostly Mediterranean species, extending from Cape Verde across North Africa and southern Europe to Greece, through the Arabian Peninsula, along the northern Black Sea coast and into Kazakhstan and northern India.
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
The species occurs in the Ru'us al-Jibal within the UAE. It is not thought to be facing any widespread threats and its population trend is likely stable. Therefore, it is assessed as Least Concern.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
There are no widespread threats.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Asplenium ceterach | UAE National Red List of Vascular Plants

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
This plant is a perennial fern with tufted fronds up to 15 cm, occurring in the Ru'us al-Jibal mountains in the UAE (Jongbloed et al. 2003, Rothfels et al. 2012). The species is generally found on cliff faces where there are seepages or where there is moisture in the air.
Taxon
Taxa
Asplenium ceterach | L.
Taxonomic Group
Plants
Taxonomic Group Level 2
Ferns and Allies
Assessed taxon level
Species
Taxon distribution as listed in assessment
Within the UAE this species has been recorded from the Ru'us al-Jibal (Jongbloed et al. 2003). Records include Jebel Jais at high elevations (M. Tsaliki pers. comm. 2019). The estimated extent of occurrence (EOO) of this species is 50-100 km<sup>2</sup>, and the AOO is likely to be very restricted (much less than 500 km<sup>2</sup>, but more than 10 km<sup>2</sup>). However, the species is likely to be under recorded and the habitat type is not well surveyed.Globally, this is a broadly distributed species and is found across the western and southern half of Europe, extending southwards and eastwards to North Africa, Yemen, Djibouti, India and China (Christenhusz et al. 2017, Board of Trustees, RBG Kew 2019).
Assessed status
Asessment status in full
Data Deficient
Assessment status abreviation
DD
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species is generally considered to be rare, with few sightings in recent years. It is only known from the Ru'us al-Jibal, which provides a restricted distribution. However, this species may benefit from or be negatively affected by climate change depending on whether rainfall and atmospheric moisture increases or decreases. Due to this uncertainty, and few records of the species in general, it is currently considered Data Deficient.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
This species could be negatively affected by climate change if rainfall and atmospheric moisture declines. However, if climate change causes increasing rainfall and atmospheric moisture, this species could benefit from the changes. Therefore, it is currently unclear whether this poses a threat to the species.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Sousa plumbea | UAE National Red List of Mammals: Marine and Terrestrial

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
The species feeds primarily over sand, but also over coral and rocky reefs. Individuals have been known to herd fish onto exposed sandbanks and apparently deliberately beach in order to seize their prey. Observations of mating and adults with calves are recorded for April and May (Baldwin 2005).
Taxon
Taxa
Sousa plumbea | (G. Cuvier, 1829)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Mammals
Assessed taxon level
Species
Taxonomic Notes
Sousa plumbea has been recognized as a species since taxonomic revision of the genus Sousa in 2014 (Committee on Taxonomy 2014, Jefferson and Rosenbaum 2014). Previously this species was lumped with the Indo-pacific Humpback Dolphin (Sousa chinensis) but animals occurring in the Indian Ocean from South Africa to India are now recognized as taxonomically distinct from those that occur further east, based on genetics, skeletal morphology, external morphology and colour. There is uncertainty about the taxonomic affinities of the Humpback Dolphins that occur in the Bay of Bengal and future studies will confirm whether S. plumbea actually occurs east of the southern tip of India.
Taxon distribution as listed in assessment
This species is found throughout the Arabian Gulf waters of UAE at depths up to 30 m. It has not so far been recorded along the UAE east coast (and is absent from the rest of the Sea of Oman as well) although it is known from the Musandam Peninsula. It is seen regularly in the Gulf where small groups are apparently resident in several areas in Abu Dhabi and Dubai coastal waters (Baldwin 2005). It occurs in Marawah Marine Biosphere Reserve, Al Yasat Marine Sanctuary, and around Sadiyat Island (Abu Dhabi) and Jebel Ali Wildlife Sanctuary (Dubai). It was seen frequently off Dubai on a 2015 survey when c. 23 individuals were identified and is sometimes seen very close inshore, such as Dubai Marina. Globally, it is found in a narrow strip of shallow, coastal waters from South Africa, through the coastal waters of East and North Africa, and the Middle East to approximately the southern tip of India and possibly further east (Braulik et al. 2017).
Assessed status
Asessment status in full
Endangered
Assessment status abreviation
EN
Assessment status criteria
A2bc
About the assessment
Assessment year
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
Preen (2004) reported a 71% decline in small species of dolphins in the Arabian Gulf from 1986 to 1999, which included: Neophocaena phocaenoides, Sousa plumbea and Tursiops aduncus. 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 S. plumbea over the past three generations (75 years). The species, therefore, qualifies for assessment as Endangered (EN) under criterion A2bc. The reduction is thought to be 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 potentially also qualifies for listing as EN under criterion C1. There is no rescue effect, as the species does not move very far; the species tends to be very localised in its occurrence.
Criteria system
Criteria system specifics
IUCN v3.1
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
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. 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). 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 and reefs. A UAE Fisheries Resource Assessment Survey in 2002 found that fish stocks in the Gulf had declined by 60%. 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.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
The backcasted 1996 assessment for this species is Endangered and under the same criterion. The Vulnerable assessment by Hornby (1996) does not appear to have taken into account the 71% decline in the species from 1986 to 1999 as reported by Preen (2004).
Verified entry
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Triaenops persicus | UAE National Red List of Mammals: Marine and Terrestrial

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
The only UAE specimens were caught in falaj tunnels. The 2017 report was from a cave.
Taxon
Taxa
Triaenops persicus | Dobson, 1871
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Mammals
Assessed taxon level
Species
Taxonomic Notes
See Benda and Vallo (2009) for a complete revision of the genus.
Taxon distribution as listed in assessment
This species was last recorded in the UAE in 1953 when a few specimens were collected in falaj (irrigation) tunnels at Buraimi Oasis, Al Ain (Harrison 1955). There was one possible sound recording in July/Aug 2017 at Ain Al Waal at the base of Jebel Hafeet (J. Judas pers. comm. 2018). The species is widely distributed in Africa, the Arabian Peninsula, Iran, and South Asia (Monadjem et al. 2017c).
Assessed status
Asessment status in full
Data deficient
Assessment status abreviation
DD
About the assessment
Assessment year
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species was last recorded in the UAE in 1953 from the Buraimi Oasis area, Al Ain, and there is a possible record from south of Al Ain from 2018 that requires confirmation. The species is assessed as Data Deficient because the last confirmed records date from 1953 and there is only one possible record in recent times. No regional adjustment is made to the Data Deficient assessment.
Criteria system
Criteria system specifics
IUCN v3.1
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
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.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
The backcasted 1996 assessment for this species is Data Deficient which matches the listing given by Hornby (1996).
Verified entry
Off

Asellia tridens | UAE National Red List of Mammals: Marine and Terrestrial

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
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).
Taxon
Taxa
Asellia tridens | (É. Geoffroy, 1813)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Mammals
Assessed taxon level
Species
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).
Assessed status
Asessment status in full
Data deficient
Assessment status abreviation
DD
About the assessment
Assessment year
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
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.
Criteria system
Criteria system specifics
IUCN v3.1
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
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.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
The backcasted 1996 assessment for this species is Data Deficient which matches the listing given by Hornby (1996).
Verified entry
Off

Cosentinia vellea | UAE National Red List of Vascular Plants

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
In the UAE, this perennial fern species is found in rock crevices at higher altitudes and growing within the shelter of boulders (Jongbloed et al. 2003, Feulner 2011). The rhizomes of the plant are covered in light brown scales, it has tufted fronds and dark green leaves covered in hair on their lower surface (Jongbloed et al. 2003). Globally this species is reported as inhabiting sunny, dry, rocky crevices, especially dolomitic, calcareous or sometimes siliceous, mostly found in hot, semi-arid, Mediterranean climates.
Taxon
Taxa
Cosentinia vellea | (Aiton) Tod.
Taxonomic Group
Plants
Taxonomic Group Level 2
Ferns and Allies
Assessed taxon level
Species
Taxon distribution as listed in assessment
In the UAE, this species is widespread in the Ru'us al-Jibal (Feulner 2011), with an additional record from Ras al-Khaimah Emirate (Diftah, southeast of Masafi), on a steep northwest-facing jebel slope above a steep-walled wadi (Rothfels et al. 2012). The species is generally considered to grow at high altitudes (Jongbloed et al. 2003). The species occurs in adjacent parts of the mountains in Oman, e.g., on Jebel Ghaweel, along the border north of Al Ain (G.R. Feulner pers. comm. 2019). Globally, the native range of this species includes Mediterranean parts of Europe and North Africa to the Arabian Peninsula and Iraq (Board of Trustees, RBG Kew 2018).
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species is generally considered to be widespread throughout rocky areas in the northeast of the UAE, in addition to growing at high altitudes where it may be subject to fewer threats. Therefore, it is assessed as Least Concern for the UAE.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
There are no widespread threats.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off