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

Cyperus rotundus | 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
It occurs in sand along the Gulf coast, and also in gardens and cultivated areas associated with fresh or slightly brackish water (Jongbloed et al. 2003).
Taxon
Taxa
Cyperus rotundus | L.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species is common along the Arabian Gulf coast of the UAE, from west of Abu Dhabi city to Ras Al-Khaimah (Jongbloed et al. 2003). The species has been recorded from Wadi Wurayah, however the origin of the species here is uncertain, and is likely to be the result of accidental introduction (Feulner 2016). Al Mehairbi et al. (2019) show a very much broader distribution for this species, across almost the entire UAE; it is thought that, if correct, this broader distribution may be the result of introduction. Globally, the species is considered to be native to the Mediterranean and throughout most of sub-Saharan Africa, east through the Middle East and Indian sub-continent to China and to Southeast Asia, south to Australia (The Board of Trustees of the Royal Botanic Gardens, Kew 2019). It occurs as a non-native in parts of Europe, the Pacific island states and through South and Central America, north to parts of the United States (The Board of Trustees of the Royal Botanic Gardens, Kew 2019). Within the Arabian Peninsula, this species is described as widespread and weedy in Saudi Arabia (Chaudhary 2001, Norton et al. 2009), common in Bahrain, Qatar (Norton et al. 2009), Oman (Ghazanfar 1992) and the United Arab Emirates (Western 1989, Jongbloed et al. 2003, Norton et al. 2009) and widespread in Yemen (Wood 1977).
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 common along the Arabian Gulf coast of the UAE. Although populations will have been impacted by habitat loss and degradation, 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
The coastal habitat of this species is impacted in the UAE by urban, industrial and touristic development.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Alepes vari | 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
This speciesoccurs in shallow coastal waters, and commonly swims near the surface forming dense schools above clear inner coral reef areas (Smith-Vaniz 1984, Kuiter and Tonozuka 2001). It feeds primarily on shrimps, copepods, decapods and small fishes. The maximum total length is 56 cm (Smith-Vaniz 1984).
Taxon
Taxa
Alepes vari | (Cuvier, 1833)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is widespread in the Indian Ocean and western Pacific (Smith-Vaniz 1984, 1999).
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 inshore, pelagic speciesis common throughout UAE waters. Fishing activity is not expected to be causing population declines at this time. There are no known major threats; therefore, it is listed as Least Concern in 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
Fishing activity is not known to be driving declines in the UAE at this time. Corals in the UAE and Arabian Gulf have severely declined due to the increasing frequency of mass bleaching events caused by rising water temperatures, which is a consequence of climate change, as well as pervasive coastal development (Riegl et al. 2018, Burt et al. 2019).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Caranx sexfasciatus | 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
This species is mostly found over coral and rocky reef complexes as adults, but is known to move into inshore areas in sandy bays and lagoons in small numbers (Hamilton and Walter 1999). Juveniles inhabit more inshore, shallower waters around the coastlines, often venturing into lagoons, tidal flats, mangroves and estuaries (Whitfield and Harrison 2003, González Acost and De La Cruz Agüero 2004). It has also been observed well into the upper reaches of rivers (Allen et al. 2002). The species has been reported in pelagic open ocean settings, milling around stationary buoys (Fedoryako 1988). It also is known to be a schooling fish, with aggregations consisting of more than 1500 fish (Sala et al. 2003). Itsdiet consists of crustaceans and fishes (Chan et al. 1974). The maximum total length is 120 cm (Frimodt 1995). The mean length at first maturity (sex unknown) is 30 cm (Tharwat and Al-Gaber 2006).
Taxon
Taxa
Caranx sexfasciatus | Quoy & Gaimard, 1825
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific (Allen and Robertson 1994, Smith-Vaniz 1995, Honebrink 2000).
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 inshore, pelagic species is common on the eastern coast in UAE waters, but is not yet confirmed from the Gulf coast. Fishing activity is not expected to be causing population declines at this time. There are no known major threats; therefore, it is listed as Least Concern in 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
Fishing activity is not known to be driving declines in the UAE at this time. Corals in the UAE and Arabian Gulf have severely declined due to the increasing frequency of mass bleaching events caused by rising water temperatures, which is a consequence of climate change, as well as pervasive coastal development (Riegl et al. 2018, Burt et al. 2019).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Sardinella albella | 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
This reef-associated, pelagic species occurs in tropical waters to a depth of 50 m. It also occurs in estuaries and mangroves (Robertson and Duke 1990). It is a schooling species considered to be an epi-pelagic planktivore (Freije and Awadh 2008). This is a short-lived species with a maximum known longevity of less than two years (Holt 1960, Sekharan 1968). It is thought to reach maturity at approximately 10 cm standard length. Its maximum standard length is 14 cm (Whitehead 1985).
Taxon
Taxa
Sardinella albella | (Valenciennes, 1847)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific (Whitehead 1985, Paxton et al. 1989, Russell and Houston 1989).According to Stern et al. (2016), no true Sardinella albella occur east of the Bay of Bengal, and those records there may represent misidentifications of S. fimbriata. This species has an estimated depth range of 0 to 50 m.
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 inshore, pelagic speciesoccurs throughout UAE waters. Fishing activity is not expected to be causing population declines approaching a Near Threatened or threatened level at this time. Although, catch is apparently declining slightly in recent years on the eastern coast, and this requires further investigation. There are no known major threats; therefore, it is listed as Least Concern in 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
Fishing activity is not known to be driving declines approaching a Near Threatened or threatened level in the UAE at this time. Corals in the UAE and Arabian Gulf have severely declined due to the increasing frequency of mass bleaching events caused by rising water temperatures, which is a consequence of climate change, as well as pervasive coastal development (Riegl et al. 2018, Burt et al. 2019).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Decapterus russelli | 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
This benthopelagic species inhabits coastal waters and open banks. Itsdiet consists of smaller planktonic invertebrates (Smith-Vaniz 1984). It attains sexual maturity at 12 cm total length in the first year of its life (Smith-Vaniz 1984). It spawns year-round, with two peak spawning periods (Balasubramanian and Natarajan 2000). The estimated longevity off India is 3.8-6.7 years (Reuben et al. 1992). The maximum total length is 39 cm (Randall 1995).
Taxon
Taxa
Decapterus russelli | (Rüppell, 1830)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific (Golani 2006).
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 inshore, pelagic speciesoccurs throughout UAE waters. Anecdotal data indicates this species may have experienced some level of decline on the eastern coast, but no catch declines are known from the Gulf coast. It remains relativwly common. There are no known major threats; therefore, it is listed as Least Concern in the UAE. It is recommended to improve fisheries monitoring of this species.
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
Fishing activity is not known to be driving declines approaching a Near Threatened or threatened level in the UAE at this time.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Alectis ciliaris | 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
This pelagic species inhabits neritic and oceanic waters. Adults are usually solitary and frequent shallow coastal waters to depths of 100 m, while juveniles are pelagic and drift. Adults are demersal, however, juveniles up to 25 cm are pelagic. Itsdiet consists of slow-swimming or sedentary crustaceans, and occasionally small crabs and fishes (Smith-Vaniz 1984). The maximum total length is 150 cm; common to 100 cm fork length (Sommer et al. 1996).
Taxon
Taxa
Alectis ciliaris | (Bloch, 1787)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Elsewhere, it is circumtropically distributed in tropical and subtropical waters (Simon et al. 2013, Smith-Vaniz 2016).
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 inshore and offshore, pelagic species is common throughout UAE waters. Fishing activity is not expected to be causing population declines at this time. There are no known major threats; therefore, it is listed as Least Concern in 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
Fishing activity is not known to be driving declines in the UAE at this time.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Sardinella longiceps | 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
This pelagic-neritic, oceanodromous species schools in tropical waters between depths of 20-200 m (al Sakaff and Esseen 1999, Riede 2004, FAO-FIGIS 2005). It feeds mainly on phytoplankton (especially diatoms), small crustaceans, plants, and benthic invertebrates (Whitehead 1985, Sommer et al. 1996). It is found at temperatures of ~22.0-28.0 '°C. Its maximum standard length is 23 cm, maturity is reached at about one year of age and the maximum reported age is 3 years (Rosa and Laevastu 1960, Bykov 1983, Whitehead 1985).
Taxon
Taxa
Sardinella longiceps | Valenciennes, 1847
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
Specimens nominally identified as this species from the Philippines and Indonesia are likely to be incorrect identifications of the similar species Sardinella lemuru (Willette and Santos 2013). Recent analysis of micro-satellite markers suggests genetic differentiation of this species between the Gulf of Oman and the coast of India (Sebastian et al. 2017). Subsequent sub-structuring of this species within India revealed genetic differentiation between samples obtained from Mumbai and Mangalore on the western coast of India and the samples obtained from the southwest and eastern coast of India (Calicut, Kollam, Trivandrum, Chennai and Vizag: Sebastian et al. 2017).
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is distributed in the northern Indian Ocean from the Gulf of Aden to the Arabian Gulf to southeast India, and possibly the Andaman Islands. Specimens from the Philippines and Indonesia are probably misidentifications of Sardinella lemuru (Froese and Pauly 2007).
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 pelagic speciesoccurs throughout UAE waters, and is globally restricted to the northern Indian Ocean region. It is heavily exploited in Iran, Oman, Pakistan and India, and severe declines have occurred over recent decades in western India, Pakistan and possibly Oman due to a combination of overexploitation and unfavorable environmental conditions. It is retained as bycatch in fisheries off the UAE and sold in markets, but is not particularly highly-valued. Its occurrence in markets has been stable over time with some suspected recent declines on the eastern coast. In general, it remains common in the UAE, but connectivity with populations outside that are apparently in decline, is poorly understood. Based on the uncertainty regarding the population trend of this exploited species, it is listed as Data Deficient in UAE waters until updated data become available. It is recommended to improve fisheries monitoring as well as the understanding of population connectivity within its range.
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
Population declines may have occurred off Oman due to exploitation and an increase in fish kill events predicated by low oxygen levels (Piontkovski and Queste 2016). Severe declines have also been reported from western India and Pakistan.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Nematalosa nasus | 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
This pelagic-neritic, anadromous species occurs in tropical waters to a depth of 30 m (Whitehead 1985, Shao and Lim 1991, Daniels 2002, Riede 2004). It is mainly found in estuaries and coastal areas, but occasionally ascends into the upper reaches of the tidal zone (Rainboth 1996). Its maximum total length is 22 cm (Whitehead and Wongratana 1986).
Taxon
Taxa
Nematalosa nasus | (Bloch, 1795)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific (Whitehead and Wongratana 1986, Munroe et al. 1999).
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 inshore, pelagic speciesis common and abundant throughout UAE waters. Fishing activity is not expected to be causing population declines at this time. There are no known major threats; therefore, it is listed as Least Concern in 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
Fishing activity is not known to be driving declines in the UAE at this time. Coastal development may be impacting the habitats of this species. It is sensitive to anoxia events, where it is frequently recorded in fish kills, but it remains abundant, and this is not considered a major threat at this time.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Balaenoptera omurai | 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?
Not possible
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
The diet, habitat, and ecology of Omura's Whales are not well known. Omura's Whales occur in both deep and shallow water, and are at least partly sympatric with Bryde's Whales.
Taxon
Taxa
Balaenoptera omurai | Wada, Oishi & Yamada, 2003
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Mammals
Assessed taxon level
Species
Taxonomic Notes
Although it was only recently described (Wada et al. 2003), the separate species identity of Omura's Whale, Balaenoptera omurai, is now well established phylogenetically (Sasaki et al. 2006). It was formerly regarded as a pygmy form of Bryde's Whale (B. brydei/edeni), but it is not closely related to that group, lying outside the clade formed by the Sei Whale (B. borealis) and two forms of Bryde's Whales). The morphology of Omura's Whale is quite distinct from those of Bryde's Whales and other known baleen whales, but its colouration resembles that of the Fin Whale (B. physalus) while lacking lateral rostral ridges (Wada et al. 2003). To date (December 2017), the only genetically confirmed observations of living Omura's Whales are of 18 biopsied individuals in an apparently resident population off northwestern Madagascar (Cerchio et al. 2015). Specimens collected in 1976 in the Solomon Sea (Ohsumi 1978) and in 1978 in the eastern Indian Ocean (Ohsumi 1980) were originally taken under a scientific permit for Bryde's Whales and were subsequently genetically identified as Omura's Whales (Wada et al. 2003). LeDuc and Dizon (2002) genetically analysed specimens of small Bryde's Whales from the Bohol Sea, Philippines, and found that they segregated phylogenetically outside the Sei/Bryde's Whale clade and basal to B. edeni/B. borealis. From a comparison of the published phylogenies, Sasaki et al. (2006) concluded that these specimens corresponded to Omura's Whale. Yamada et al. (2008) identified 24 skulls from a whaling operation in the Philippines as Omura's Whales.
Taxon distribution as listed in assessment
The occurrence of Omura's Whale in UAE waters is unconfirmed and very poorly known. One of the two stranded whales found in March 2018 at Ras Al Khaimah might be this species (R. Brownell Jr. pers. comm. 2018). There is one record from Iranian waters just in the Arabian Gulf (Ranjbar et al. 2016) and the next closest is from the Red Sea (Egypt), so it may be present off the east coast of the UAE.The global range of Omura's Whale requires further research because very few specimens have been confirmed to date. The type specimen was a stranded individual collected near Oyama in the southern Sea of Japan in 1998 (Wada et al. 2003). Confirmed specimens and suspected sightings recorded to date are listed by Cerchio et al. (2017). The only genetically confirmed population of living Omura's Whales to date occurs off northwestern Madagascar (Cerchio et al. 2015) on the shallow continental shelf, mainly in the 10-25 m depth range. Photographs of living whales taken off New Caledonia appear to show Omura's Whales, and there have also been suspected live sightings off eastern Australia. Omura's Whales are at least partially sympatric with Bryde's Whales and occur both in deep water and in inshore areas. All records to date have been between 35'°N and 35'°S. It is unclear whether Omura's Whale is mainly a coastal species or if a substantial oceanic population exists.
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
The global range of this recently described species, Balaenoptera omurai, is poorly known, and no estimates of abundance are available. Within UAE waters, the species is recorded from a single unconfirmed stranding in Ras Al Khaimah in March 2018 (R. Brownell Jr. pers. comm. 2018). Given the scarcity of records of the species from the UAE plausible categories span from Critically Endangered to Least Concern, and hence following IUCN guidelines the species is assessed for the UAE national Red List as Data Deficient.No regional adjustment is made to the Data Deficient assessment.
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
Given its occurrence in shallow waters, it may be subject to entanglement or bycatch and vessel strikes. Because the species has only recently been described and its range is poorly known, it is not yet possible to assess the type, level or extent of any threats.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
The backcasted 1996 assessment for this species is Data Deficient if its existence back then had been known.
Verified entry
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Acomys dimidiatus | 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
Predominantly crepuscular and nocturnal and prefers all kinds of rocky habitats (Harrison and Bates 1991). Found on boulder-strewn slopes and rocky terrain where it lives in crevices among boulders (Cunningham 2008) and in wadi beds in Wadi Wurayah (Judas 2016). In a community structure study of Jebel Al Jais in Ras Al Khaimah Emirate, the species was recorded at elevations ranging from 450-“1,650 m, was most abundant in the wadi area around 450 m, and its abundance declined with increasing altitude (Melville and Chaber 2016). It was trapped at around 180 m asl on he outlying hill of Jebel Nazwa (Qarn Nazwa) in 2018 (J. Judas pers. comm. 2018). This species is omnivorous (Melville and Chaber 2016). There is evidence from trapping surveys that the Arabian Spiny Mouse is more susceptible than other small mammal species to disturbance and fragmentation (B. Howarth pers. comm. 2018).
Taxon
Taxa
Acomys dimidiatus | (Cretzschmar, 1826)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Mammals
Assessed taxon level
Species
Taxonomic Notes
Formerly considered a subspecies of Acomys cahirinus. See Musser and Carleton (2005) for details concerning the relationship between Acomys dimidiatus and A. cahirinus.
Taxon distribution as listed in assessment
This species was first recorded for the UAE in 1971 at Jebel Faiyah, Sharjah, and then again in 1991 when a dead specimen was found by a road near Ghayl, Ra's al Khaimah. Subsequent surveys have shown that this species is quite widespread and numerous through the Hajar Mountains at lower elevations, particularly where Acacia tortilis is present. The species is also found on Jebel Hafeet, where it occurs at all elevations including barren rocks near the summit (Aspinall et al. 2005). It has also been recorded at several sites in Ras Al Khaimah (RAK Nature pers. comm. 2018) and on Qarn Nazwa in Dubai Emirate. Globally, this species is distributed from the Sinai Peninsula of Egypt through much of the Arabian Peninsula to Iran and southern Pakistan (Cassola 2016a).
Assessed status
Asessment status in full
Near threatened
Assessment status abreviation
NT
Assessment status criteria
B1b(iii)
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
Within the UAE, this species is restricted to rocky areas, primarily the Hajar Mountains, Jebel Hafeet and Qarn Nazwa. The extent of occurrence (EOO) is just over 6,000 km<sup>2</sup>, there is a continuing decline in the extent and quality of habitat due to a variety of threats, however, the number of locations is more than ten and the range is not severely fragmented, so it is assessed as Near Threatened (close to qualifying for a threatened category under criterion B1ab(iii)). There might be some rescue effect from populations in adjoining countries, particularly Oman, but this is not thought to be significant hence the regional assessment is not adjusted.
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
Overgazing, quarrying, road construction and other development activities in the mountains result in habitat loss and degradation and increased fragmentation. Species in the mountains may also be affected indirectly by falling water tables due to over-abstraction and reduced precipitation. An increase in numbers of feral cats and Red Foxes may also pose a threat to all small mammals.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
The backcasted 1996 assessment for this species is Near Threatened (almost meets a threatened listing under criterion B1ab(iii)) which matches the listing given by Hornby (1996).
Verified entry
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