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

Plantago notata | 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?
Not possible
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
This annual species is described as 'woolly', without a stem and with crowded leaves at the base of the plant (Jongbloed et al. 2003), and distinguished by its toothed leaves. Feulner (2011) commented that its scattered occurrences in the Ru'us al-Jibal were mostly ruderal. Karim and Fawzi (2007) recorded it from Al-Ain in sandy soil.
Taxon
Taxa
Plantago notata | Lag.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species has been recorded from scattered locations in the Ru'us al-Jibal (Western 1989, Jongbloed et al. 2003, Feulner 2011). In that area it has been recorded at high elevations up to around 1,500 m (Feulner 2011). It was also recorded as 'rare' in the Al-Ain area (Fawzi and Karim 2007). Although Plants of the World Online lists the UAE as a native country of occurrence for this species (Board of Trustees, RBG Kew 2019), a more detailed distribution of this species within the country is lacking. The species is not recorded from Oman, and the identity of records from the UAE require confirmation (S. Ghazanfar pers. comm. 2019). Globally, the native range of this species extends from Spain across northern Africa to the Arabian Peninsula and Iran (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
There is little information available on this species, including lack of its detailed distribution within the UAE. Therefore, it is assessed as 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
There is no information available.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Plantago ciliata | 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 annual herb species grows within compact sand, on hillsides, in gravel terraces and in plantations (Jongbloed et al. 2003, Mousa and Fawzi 2009, Feulner 2016, Mahmoud et al. 2018). This is a low plant with virtually no stem and the leaves crowded in a rosette form. The leaves are oval in shape in addition to the fruit, while the flowers are small, cream-coloured and present between February and April (Jongbloed et al. 2003).
Taxon
Taxa
Plantago ciliata | Desf.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
Within the UAE, this species is widespread within the northern and central desert of the country (Jongbloed et al. 2003). It is also known to occur in the Ru'us al-Jibal at elevations up to 1250 m (G.R. Feulner, in litt, MEW 2010, Feulner 2011). Globally, this species is native to Africa, Pakistan and temperate Asia (Board of Trustees, RBG Kew 2019).
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 widespread throughout central UAE, in addition to occurring within the Ru'us al-Jibal. It is considered locally common in these areas and is also recorded from at least one protected area within its range. It is therefore 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 is in information available.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Plantago boissieri | 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 annual herb species is known to grow within saline and coastal sand dunes in the UAE (Jongbloed et al. 2003, Karim and Dakheel 2006, Brown et al. 2007, Mahmoud et al. 2018), although it has also been described as a weed in old fields in Oman (Western 1991). It can reach up to 0.2 m in height, has linear to lanceolate shaped leaves with fine silky hairs, in addition to long cylindrical spikes with very small white-green flowers which can be seen between January and April (Jongbloed et al. 2003, Karim and Dakheel 2006). It is a moderately salt-tolerant species (Karim and Dakheel 2006) and has been described as one of the most important contributors to biomass in dune and stabilised sand environments (Ghazanfar and Fisher 1998).
Taxon
Taxa
Plantago boissieri | Hausskn. & Bornm.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
Within the UAE, it is described as occurring along the Arabian Gulf coastline (Brown et al. 2007). Jongbloed et al. (2003) shows a wide distribution from gravel plains west of the Hajar Mountains, south and west into Dubai Emirate. Globally, the native range of this species encompasses temperate Asia and the Arabian Peninsula (Board of Trustees, RBG Kew 2019).
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 widespread within sandy areas inland from the Arabian Gulf Coast of the UAE. Within these areas, it is locally common and is abundant, perhaps even a dominant species, in some areas. As such, it is therefore 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
Grazing, urban development, and road construction are likely to impact the species.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Plantago amplexicaulis | 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 annual herb species grows on hillsides and in plains, generally in sandy and silty areas (Jongbloed et al. 2003, MEW 2010, Mahmoud et al. 2018). The plant can reach up to 30 cm in height, has lance-shaped leaves in a basal rosette, in addition to an elliptic fruit containing two brown seeds and white, densely packed flowers which are present between February and May (Jongbloed et al. 2003).
Taxon
Taxa
Plantago amplexicaulis | Cav.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
Within the UAE, it is known to occur in the Hajar Mountain range and in the south of the Ru'us al-Jibal (Jongbloed et al. 2003). In the Ru'us al-Jibal it is recorded at elevations of up to 1600 m (G.R. Feulner, in litt, MEW 2010, Feulner 2011), while in the Hajar Mountains it is found at lower altitudes (MEW 2010). Globally, the native range of this species encompasses the Mediterranean, northern Africa and the Arabian Peninsula (Board of Trustees, RBG Kew 2019).
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 widespread throughout the Hajar Mountains and the Ru'us al-Jibal. Within these areas, it can occur at a range of altitudes and is considered to be locally common within the Hajar Mountains. In addition, it is known to occur in at least one protected area within its range. 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 is no information available.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Seidlitzia rosmarinus | 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 small, perennial shrub species is considered to be a halophyte and is found growing in sandy plains in addition to both coastal and inland sabkha, or saltflats (Jongbloed et al. 2003, Böer and Saenger 2006, Karim and Dakheel 2006, Qureshi 2017). It can grow up to 60 cm in height, has a woody base, succulent club-shaped leaves and clustered flowers which can be seen between October and December (Karim and Dakheel 2006). This plant is also regularly grazed by camels (Böer and Saenger 2006).
Taxon
Taxa
Seidlitzia rosmarinus | Bunge. ex Boiss
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
Within the UAE, this species is known from the Liwa region and towards the far west of the country, along the Arabian Gulf coast (Jongbloed et al. 2003). This species is native to Egypt, the Arabian Peninsula and through to Afghanistan (Board of Trustees, RBG Kew 2019).
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 considered to be locally common within the UAE and seems to be quite widespread. 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
This plant is regularly grazed by camels (Böer and Saenger 2006).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Silene villosa | 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 species is an annual herb species which can grow up to 45 cm in height (Jongbloed et al. 2003, Norton et al. 2009). Between February and April, it produces white flowers which open during the evening and at night time (Jongbloed et al. 2003). This species can be found growing within stable sand and in between dunes (Jongbloed et al. 2003) and is considered to be an important contributor to biomass in these environments (Ghazanfar and Fisher 1998).
Taxon
Taxa
Silene villosa | Forssk.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
Within the UAE, this species is widespread throughout sandy and coastal areas in the north of the country and down to Al Ain (Jongbloed et al. 2003). It is also thought to occur on some islands within the UAE (MEW 2010). Globally, the native range of this species spans from northern Africa and the Sahara to the Arabian Peninsula (Board of Trustees, RBG Kew 2019).
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 considered to be widespread throughout the UAE, and is described as common throughout this range. It is an important and characteristic species of sand dune environments. Although it may be threatened by over-collection, over-grazing and habitat loss, it is unclear to what extent this currently affects the species. It is therefore 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
This species may be threatened by habitat loss, over-collection and over-grazing (Heneidy et al. 2018).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Paronychia arabica | 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 annual herb species grows within sand and silt substrates between rocks in wadis, in addition to on wadi banks and in fallow fields (Fawzi and Ksiksi 2012, Mahmoud et al. 2018). It can grow up to 30 cm in height, has narrowly oblong leaves and small white flowers which are present between February and April (Jongbloed et al. 2003).
Taxon
Taxa
Paronychia arabica | (L.) DC.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
Within the UAE, this species is thought to occur along a specific stretch of the Arabian Gulf Coast, between Abu Dhabi island and Ras al-Khaimah (Brown et al. 2007). It was also recently reported from Jebel Hafeet (Sakkir and Brown 2014) and is considered to grow within the non-saline coralline sands which stretch northeast of Taweela and into the Ras al-Khaimah (G. Brown pers. comm. 2019). Globally, the native range of this species spans from northern Africa to the Arabian Peninsula (Board of Trustees, RBG Kew 2019).
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 common, appears to be fairly widespread and occurs within at least one protected area in its range. It is therefore 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 is no information available.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Gazella arabica | 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
Arabian Gazelle occurs in deserts, semi-deserts, hills, mountains and coastal plains, often being associated with Acacia. It is generally seen singly or in small groups.
Taxon
Taxa
Gazella arabica | (Lichtenstein, 1827)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Mammals
Assessed taxon level
Species
Taxonomic Notes
The taxonomy of genus Gazella is complex and several different arrangements have been proposed, but several issues remain unresolved. Gazella arabica was originally described from a single specimen: a skin and a skull obtained on the Farasan Islands off the coast of Saudi Arabia (or at least labelled as such). This became something of a mystery taxon and is different from the gazelles currently found there. Bärman et al. (2012) extracted DNA from the type specimen and showed that this was not a single specimen, assigning the skin to G. g. cora and the skull to gazelles of the northern type (G. g. gazella). Wronski et al. (2010) showed that Gazella gazella, in fact, consists of two monophyletic lineages, a northern clade (represented by samples from the Golan Heights) and a southern clade (based on samples from the Arabian Peninsula including the southern Arava Valley), based on mtDNA markers. Lerp et al. (2012) produced similar conclusions using nuclear markers and including samples from Central Israel. A morphological and genetic study of genus Gazella (Bärmann et al. 2013), and a genetic study of gazelles in the southern Levant (Hadas et al. 2015) all further support the existence of two monophyletic lineages: a northern clade (Gazella gazella), and a southern clade (provisionally named G. arabica on the basis that this name takes precedence over cora). This arrangement is now followed by the IUCN SSC Antelope Specialist Group, with G. gazella replacing G. g. gazella in the former arrangement, and the name G. arabica provisionally retained for the southern clade, pending a ruling by the International Commission on Zoological Nomenclature (ICZN). So G. arabica, as understood here, comprises all the gazelles formerly considered under G. gazella, from the southern Negev through the Arabian Peninsula. Several subspecies have been named under G. gazella and have previously been evaluated for The IUCN Red List: acaciae; in the southern Arava Valley; cora in most of the Arabian Peninsula; farasani on the Farasan Islands; and muscatensis on the Batinah coast of Oman. Genetic research by scientists at King Khaled Wildlife Research Centre (Saudi Arabia) and Zoological Society of London (ZSL) has confirmed the existence of some intraspecific variation, but there is no agreement on the validity of these named subspecies and they are not assessed separately for the time being, until a definitive analysis has been produced. All of the above are included in G. arabica here. The relationship between G. arabica (as here) and two other 'mystery' species, G. erlangeri and G. bilkis awaits confirmation.
Taxon distribution as listed in assessment
Formerly widespread in UAE but then its range became reduced. Around 15-25 years ago it was known from a few sites in the Hajar Mountains and large areas of desert between Jebel Ali and Sweihan (Hornby 1996, Aspinall et al. 2005). Sites in the mountains include Gulfa Wadi (Masfut), Wadi Jabsah (Fujairah), and on the ridges above Wadi Awsaq, on the southern edge of the Musandam (in the mid-1990s). At the same time, gazelles were present in neighbouring Oman in Wadi Qahfi (near the so-called Hatta Pools); in several wadis with permanent water along the mountain front south of the Hatta road; and in the remote high Musandam, east of Jebel Harim). Musandam records from the late 2000s in the area near the watershed between Wadi Bih and Wadi Khabb Shamsi are believed to represent releases (a pair of animals was found in the same locality at ca. 1,200 m in two successive years). Some of the remaining desert subpopulations have also been supplemented by releases from captive breeding programmes, in some cases, such as the Dubai Desert, since the mid-1990s. The Al Marmoom Conservation Area and adjacent areas of the Dubai Desert hold one of the largest current subpopulations. This area also holds Oryx leucoryx and Gazella marica. The area is provisioned by the Dubai Municipality and the Ruler's Office with alfafa and water, but oryx tend to dominate the feeding points while the gazelles range widely over the whole area. Mountain Gazelles have also been released in the Dubai Desert Conservation Reserve, on Siniyyah Island, Arabian Oryx Protected Area and at other sites in Abu Dhabi Emirate. Based on the known habitat preferences, it is assumed that historically G. marica occupied desert areas and G. arabica the mountains and their fringes, but releases may now have obscured the original pattern. The species is endemic to the Arabian Peninsula, where it was once widely distributed. The largest remaining subpopulations are found in Oman and on the Farasan islands in Saudi Arabia. It has been reintroduced to the Uruq Bani Ma'arid, Mahazat as Sayd, and Ibex Reserves in Saudi Arabia. There is a small introduced subpopulation on Farur Island, Iran (IUCN SSC Antelope Specialist Group 2017a).
Assessed status
Asessment status in full
Least concern
Assessment status abreviation
LC
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 species was formerly widespread in the UAE but its range and population size are much reduced, however, conservation efforts, captive breeding and releases have resulted in the population stabilising and now increasing. As a conservative estimate, the population is estimated to contain over 1,500 mature individuals and the population is stable or increasing, so the species does not qualify for a threatened category or Near Threatened and is assessed as Least Concern. No regional adjustment is made to the Least Concern 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
Uncontrolled hunting is considered responsible for the decline of the species across its regional range. Overgrazing is also a major factor in many areas (IUCN SSC Antelope Specialist Group 2017a). The increasing construction of roads and fences has likely had a serious impact on the habitat through fragmentation and preventing access to the limited supplies of water. There may be a risk of infectious diseases such as PPR, brucellosis, through contact with domestic livestock.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
Over the last 15-25 years, captive breeding, releases and reinforcement, and the establishment of a network of protected areas has resulted in a large and stable population. Hornby (1996) listed Gazella gazella cora as Vulnerable and the backcasted 1996 assessment for this species is also Vulnerable under criteria C2a(i); D1.
Verified entry
Off

Nannorrhops ritchieana | 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?
Incomplete
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
This plant species is described as perennial tree with fan-shaped leaves forming clumps several meters across that generally occurs in gravelled areas along low wadi banks (Jongbloed et al. 2003). According to G.R. Feulner (in lit, MEW 2010), the species is normally found at places where wadi broaden and silt accumulates.
Taxon
Taxa
Nannorrhops ritchieana | (Griff.) Aitch.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
Within the UAE, this species occurs along the western slopes of the Hajar Mountains from Shawka, south to the border with Oman (Jongbloed et al. 2003, Feulner 2011). The species also occurs on Jebel Hafeet (Perry 2008) on the northern summit wadi on Jebel Hafeet (at almost 1,000 m asl; G.R. Feulner, in lit. MEW 2010), where it persists (S. Sakkir and G. Brown pers. comm. 2018). According to G.R. Feulner (in lit. MEW 2010), this species ""is consistently present as one or a few clumps/groves in almost every wadi from Shawka south [to the Oman border], normally at places where the wadi broadens for one reason or another and silt accumulates. It is relatively common in the wadis in the greater Juwaif area, about half-way between the Hatta Road and Mahdhah."" The Sharjah Seedbank & Herbarium (SSBH) recorded the species from the Al Dhaid-Masafi road (Thaoban), and found four new clumps of the plant in Al-Bardy and Al-Wishah (in gravelly area east of Dhaid); these clumps are located inside farms, and local people reported that ""...they planted it"" a long time ago (T. Mahmoud pers. comm. 2019). The EOO is estimated at between 1,500 and 2,000 km<sup>2</sup>, whilst the AOO is less than 500 km<sup>2 </sup>and is likely to be as little as 300 km<sup>2</sup>. The species also occurs in adjacent areas of Oman (G.R. Feulner in lit. MEW 2010). Globally, the species is native from the southern Arabian Peninsula to Iran and Pakistan (Board of Trustees, RGB Kew 2018).
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
Assessment status criteria
B1a+2a
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
Within the UAE, this species occurs in the Hajar Mountains from Masafi (Wadi Ham south to the border with Oman, including Wadi Hatta), and also occurs on Jebel Hafeet. some subpopulations may be the result of intentional cultivation for use. The extent of occurrence (EOO) is between 1,500 and 2,000 km<sup>2</sup>, and the AOO at less than 500 km<sup>2</sup>. There is no information on population size or trend. The species is assessed as Near Threatened as, whilst the extent of occurrence (EOO) and area of occupancy (AOO) are restricted, and it is suspected that the species occurs in between eight and ten locations, there is no evidence of widespread threats within its distribution range, or of continuing decline. The species would qualify as Vulnerable if a continuing decline in the number of mature individuals, or in habitat area, extent or quality was known or suspected. In addition, the species might potentially qualify as threatened under criterion D, however further information on the population structure of this probably clonal species is required.
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
MEW (2010) considered populations fragmented and at threat from development, without giving details. At one site in the Hajar Mountains, quarrying activities had lowered the wadi floor by at least 2 m, with consequential impacts on the ground water level. As a result, one cluster of the palm in the wadi is dying (D. Aplin pers. comm. 2019). The species is generally found in the lower parts of wadis and it is therefore vulnerable to development, e.g. road construction, and other works.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
The situation for this species in 1996 is thought to be similar to the situation for the species now.
Verified entry
Off

Mobula mobular | 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 Giant Devil Ray is mostly oceanic, but is also known to occur in coastal waters (Last et al. 2016). This species reaches a maximum size 520 cm disc width (DW) with males mature around 198-205 cm DW and females around 236 cm DW (Weigmann 2016, Last et al. 2016). As is the case with other members of the genus, this species is livebearing and histotrophic, with embryonic nutrition supplied from a protein- and lipid-rich histotroph from highly developed trophonemata. A single, relatively large pup is produced per litter (Compagno and Last 1999, White et al. 2006b). Intrinsically, Manta and Mobula rays have among the lowest productivity of any chondrichthyan due to their large size, low fecundity, and late age at maturity (Pardo et al. 2016). Long resting periods may account for extended reproductive cycles in mobulid species. The generation length of this species is suspected to be around 20 years, based on the Reef Manta Ray (Manta alfredi), which reaches a similar size, is 25 years (Marshall et al. 2009).
Taxon
Taxa
Mobula mobular | (Bonnaterre, 1788)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
Recent revisions of the taxonomy of genus Mobula included the decision to consider the circumglobal Spinetail Devil Ray M. japanica (Müller & Henle, 1841) a junior synonym of the Mediterranean Giant Devil Ray M. mobular (Bonnaterre, 1788), causing M. mobular to become a circumglobal species (Poortvliet et al. 2015, Hosegood et al. 2018, White et al. 2018).Notarbartolo di Sciara et al. (2020) argued that one of the traits that were used to support the differentiation between the two species, the maximum size of M. mobular purportedly in excess of 5 m disc width (DW), can be explained by past misidentifications of M. birostris, and therefore unsubstantiated. This also supports their recommendation to retain for the species the common name Spinetail Devil Ray instead of Giant Devil Ray.
Taxon distribution as listed in assessment
The Giant Devil Ray occurs throughout UAE waters. Elsewhere, it is probably circumglobal in tropical and subtropical waters (Notarbartolo di Sciara et al. 2017).
Assessed status
Asessment status in full
Vulnerable
Assessment status abreviation
VU
Assessment status criteria
A2d
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 Giant Devil Ray occurs throughout UAE waters. This species is not targeted or valued in markets of the UAE and capture of this species is totally banned in the UAE. It is a component of the bycatch in several fisheries, but much of this catch is unreported. It is directly targeted in Sri Lanka and India, and exported to international markets, especially China where the gill plates are highly-valued. Its low productivity causes it to be susceptible to rapid population declines. 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. There is no information to confirm that this species is breeding in the UAE and no information confirming the likelihood of a cease in immigration from outside the region, despite ongoing threats and recorded declines. Based on recorded levels of exploitation, it is suspected to have declined by 30-50% over the past three generation lengths, or about 60 years. It is listed as Vulnerable A2d.
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
Information pertaining to threats specific to the UAE are unavailable. This species is impacted by target (for fins and their valuable meat) and bycatch fisheries that are active elsewhere in its range. Manta rays are easy to target because of their large size, slow swimming speed, aggregation behaviour and predictable habitat use.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off