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

Pomadasys stridens | 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 speciesinhabits soft bottoms in coastal waters (Carpenter et al. 1997b), including estuaries (Kamrani et al. 2016). Its maximum total length is 21 cm (Safi et al. 2014). In Iran, the mean total length at first sexual maturity is 19.84 cm (Vahabnezhad et al. 2018).
Taxon
Taxa
Pomadasys stridens | (Forsskål, 1775)
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 restricted to the Western Indian Ocean where it occurs from South Africa to Mozambique (McKay 1984) and the Red Sea to the Arabian Gulf (B. Russell, K. Carpenter and Y. Iwatsuki pers. comm. 2013), Pakistan (Psomadakis et al. 2015) and questionably in western India (Smith and McKay 1986, Iwatsuki et al. 1995). Its depth range is 0-68 m.
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 inshore, marine and estuarine species occurs throughout UAE waters. It is apparently less common in the Arabian Gulf, than on the eastern coast. Its occurrence in fish markets has apparently declined over time on the eastern coast. It can be impacted by estuarine degradation (e.g., Egypt). Based on the uncertainty from impacts on estuarine degradation/pollution and the possibility for overfishing on the eastern coast, it is listed as Data Deficient in the UAE. Improvements in fisheries monitoring are needed.
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
Overfishing is a potential major threat. The inshore habitats, including estuaries, that this species is dependent on have experienced large-scale degradation in the UAE and surrounding areas. It is susceptible to deformities caused by adverse environmental conditions according to a study conducted off Iran (Alavi-Yeganeh et al. 2019).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
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Alepes djedaba | 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 large schools and is common near inshore reefs and open sand patches, sometimes in moderately turbid water (Smith-Vaniz 1984, Thomas et al. 2012). Itsdiet consists of shrimps, copepods, larvae of decapod crustaceans and small fishes (Smith-Vaniz 1984). Sexual maturity is reached between 17 and 18.9 cm (Smith-Vaniz 1984, Kasim 2003) and the maximum total length is 40 cm (Heemstra 1995). Spawning takes place in December and September with recruitment in June and March (Kasim 2003).
Taxon
Taxa
Alepes djedaba | (Forsskål, 1775)
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 (van der Elst 1993, Eschmeyer 2014). This is a reef-associated and amphidromous (Riede 2004), shallow water fish, but the exact depth range it occupies is unknown.
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 in 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
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Aristolochia bracteolata | 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 a perennial or annual plant that grows up to 2 m. It flowers between February and June and is found in plantations and disturbed ground. Plants of the World Online (Board of Trustees, RBG Kew 2018) report the growth form to be a small shrub.
Taxon
Taxa
Aristolochia bracteolata | Lam.
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 only known from two localities; a plantation at Lulayah near Khor Fakkan (Western 1987) on the east coast, and from Al Ain near Jebel Hafeet (Jongbloed et al. 2003). Continued presence at both sites requires verification, given the age of the records and the extensive commercial and urban development that has occurred at both localities in recent years. Globally, this species occurs in Central and East Africa, through the Arabian Peninsula, to Pakistan and India (Board of Trustees, RBG Kew 2018).
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
Within the UAE, this species is only known from two old records; a plantation at Lulayah near Khor Fakkan (Western 1987) on the east coast, and from Al Ain near Jebel Hafeet (Jongbloed et al. 2003). No further information is available, other than that it was found in a plantation and in the disturbed ground. Whilst the species is reported to be native to the UAE, this perhaps requires confirmation given the few records and its medicinal applications. Continued presence at both sites requires verification, given the age of the records and the extensive commercial and urban development that has occurred at both localities in recent years. It is therefore considered Data Deficient 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 has been extensive commercial and urban development at both localities, which poses a threat to this species.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Lindenbergia indica | 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
The species is found in wadis and on hillsides (MEW 2010). The typical locality is at base of gravel wadi walls (Feulner 2016). It is a perennial with a woody base that reaches up to 0.3 m in height (Jongbloed et al. 2003).
Taxon
Taxa
Lindenbergia indica | (L.) Vatke
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
In the UAE, the species occurs in the southern Hajar Mountains and on Jebel Hafeet (Jongbloed et al. 2003). The species is absent from the Ru'us al-Jibal (Feulner 2011). There is a single historical record of two plants from a tributary of mid-Wadi Zikt in the Wadi Wurayah National Park buffer zone (Feulner 2016). Gillet (2006) recorded the species from Wadi Khutwa near Al Ain, but it is uncertain if this record is from within the UAE. In the Arabian Peninsula, the species is known from Oman, Saudi Arabia and Yemen (Hjertson 1995), and the United Arab Emirates (Jongbloed et al. 2003). The global range of this species is from the eastern Mediterranean to through Egypt to north-east Africa, and through the Arabian Peninsula to Thailand (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 moderately widespread in the north-eastern of the UAE and qualifies 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 by livestock may impact the species in parts of its range.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Polygonum argyrocoleon | 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 species is known to grow within plantations (Jongbloed et al. 2003, MEW 2010). It is an annual herb species and produces clustered pink flowers (Jongbloed et al. 2003, Norton et al. 2009, MEW 2010). Polygonum argyrocoleon appears to prefer moist ground and has been referred to as a weed (Norton et al. 2009).
Taxon
Taxa
Polygonum argyrocoleon | Steud. ex Kunze
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species is described as being 'widespread' within the UAE and growing within plantations (Jongbloed et al. 2003). In addition, R. Western recorded this species from Abu Dhabi. The global distribution of this species is uncertain. GRIN (2019) considers it to be native to West Asia (Afghanistan, Iran, Iraq), Central Asia, western China and the Caucasus, introduced and naturalised elsewhere. Plants of the World Online (Board of Trustees, RBG Kew 2019), gives the native distribution as northern Africa, the Arabian Peninsula and central Asia. In the Arabian Peninsula, this species is known from Saudi Arabia, United Arab Emirates, Qatar and Kuwait (Miller and Cope 1996). There don't appear to be any current specimens collected from the UAE within the Royal Botanic Garden Edinburgh's Herbarium collection (RGBE Edinburgh 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 for this species. Its population status and trends, in addition to its threats and specific distribution, are unknown, and it may be introduced to the UAE. It is assessed as Data Deficient. Confirmation of the origin, distribution and population status of this species is needed.
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

Verbascum akdarense | 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
There is no information available.
Taxon
Taxa
Verbascum akdarense | (Murb.) Hub.-Mor.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxonomic Notes
The species name is sometimes miss-spelt as 'akhdarense'.
Taxon distribution as listed in assessment
This species is recorded for the UAE by the draft Red Data Book (MEW 2010), however no distribution data has been found. G.R. Feulner has not recorded the species for the UAE (pers. comm. 2019). This species has been considered to be restricted to the mountain areas in northern Oman, where it is found in the Western and Eastern Hajar Mountains (Huber-Morath 1984, Patzelt 2014), however, according to S. Ghazanfar (pers. comm. 2019), the species is found in northern Oman, on the mountains, on rocky slopes and mountain sides, amongst rocks, and in crevices, from 400 to 1,800 m elevation, and extends into the UAE.
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
Confirmation of the presence of this species in the UAE is needed, and it is considered to be 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
Without detailed information on the distribution in the UAE, little can be said about threats.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Schweinfurthia imbricata | 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 is a prostrate, spreading, annual species with round, dark green, overlapping leaves (Feulner 2016). It is found on sandy and gravelly plains and in the lower parts of wadis and wadi outwashes.
Taxon
Taxa
Schweinfurthia imbricata | A.G.Mill., M.Short & D.A.Sutton
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
Jongbloed et al. (2003) presented only a single record (Wadi Siji) for the UAE, with MEW (2010) recording three unspecified sites. However, since then the species has been found at numerous sites within the Hajar Mountains. Records include Wadi Wurayah National Park (WWNP; Feulner 2016, Judas 2016), the gravel outwash on the UAE side of the border from Wadi Agram (Gardner 2009), from the gravel plains in the vicinity of Jebel Hafeet (Sakkir and Brown 2014, EAD 2018) and Wadi Helo (El-Keblawy et al. 2016). Mahmoud et al. (2018) found the species in gravel plains and wadis in their recent study of dams along the western slopes of the Hajar Mountains, without specifying the localities. The Sharjah Seedbank & Herbarium holds six records from the UAE: Wadi Al Nahwa (Nahwa), Sharjah-kalba Road and Shawka (Ras Al Khaimah), Sayh Mudayrah (Ajman), Al Khudairah, Al Dhaid (Sharjah) and Fili. In the WWNP, the two specimens were found in synanthropic areas (the picnicking area below the Wadi Wurayah waterfall and in the silt behind the Wadi Wurayah dam; Feulner 2016), meaning the origin of the species in the park may require confirmation. Due to the absence of precise locality data for some records, it is difficult to accurately estimate the EOO and AOO. However, it is suggested that the EOO is likely to be less than 5,000 km<sup>2</sup> and the AOO less than 100 km<sup>2</sup>. This species is endemic to Oman and the UAE (Patzelt 2014). Within Oman, it is found in the north (Western and Eastern Hajar Mountains) and in the centre, on Masirah Island.
Assessed status
Asessment status in full
Endangered
Assessment status abreviation
EN
Assessment status criteria
D
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 endemic to Oman and the UAE, and in the UAE, it is restricted to the southern parts of the Hajar Mountains and to the gravel plains around Jebel Hafeet. Whilst Jongbloed et al. (2003) presented only a single record (Wadi Siji) for the UAE, the species has since been found at numerous further sites within the country in the Hajar Mountains. Overall, there are estimated to be less than 250 mature individuals within the UAE, which meets the thresholds for Endangered under Criterion D. It has a restricted area of occupancy (AOO) and extent of occurrence (EOO), in addition to undergoing a decline in the extent and quality of habitat. However, as it is considered to occur at ten threat-based locations, it exceeds the thresholds for Endangered under Criteria B1 and B2. Therefore, this species is assessed as Endangered according to its small population size. Although there are populations of this species in adjacent parts of Oman (e.g. south of Hatta to at least Wadi Jizzi in Oman), it is not know if there are significant immigration of propagules to the UAE population. Therefore, no regional adjustment 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
No
Endemism Notes
Is an endemic?: No
Endemism specifics: This species is endemic to Oman and the UAE
Conservation
Threats listed in assessment
MEW (2010) found that road construction will likely impact one known site. Gardner (2009) found the Wadi Agram site to be heavily degraded by gravel extraction and by camel grazing, with numerous camel farms in the area. Grazing is likely to be a common threat across the range of Schweinfurthia imbricata, with other threats including off-road driving and general development pressure.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
The situation of this species in 1996 is considered to be similar to the current situation. It is considered to have remained as 'Endangered' due to its small population size.
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Rumex limoniastrum | 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
An erect to semi-pendant small shrub, typically found on ledges, walls or other sites protected from browsing (Feulner 2016), but also found on wadi floors, for example, after rains. The seed may be wind-dispersed, but within short distances (D. Aplin pers. comm. 2019) and also to some degree through consumption by animals.
Taxon
Taxa
Rumex limoniastrum | Jaub. & Spach
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxonomic Notes
Described from the type collection on Jabal Al Akhdar (Oman) in 1844 and in Oman not collected since. It is closely related to R. nervosus Vahl and may prove to be conspecific (Miller and Cope 1996). More collections are required to confirm its taxonomic position. Until then the status of this species remains doubtful.
Taxon distribution as listed in assessment
In the UAE, this species is found in the Hajar Mountains, where G.R. Feulner (in litt, MEW 2010) reports it from a small number of records, although Feulner (2016) considered it to be widespread in the mountains but very rare. Two specimens are known from the Wadi Wurayah National Park (WWNP) area: a historical record from the upper Wadi Siji in the WWNP buffer zone, and one from the upper Wadi Zikt (Feulner 2016). <a href=""http://data.rbge.org.uk/herb/E00181462"">RBGE Herbarium</a> hold one specimen from five kilometres southeast of Masafi, below Jebel Masafi. A further record is known from Wadi Hatta and Jebel Hatta. Both the EOO (&lt;310 km<sup>2</sup>) and the AOO (&lt;100 km<sup>2</sup>) are highly restricted.This species is restricted to northern Oman and the UAE. In Oman, it is found in the Jabal Al Akhdar range of the Western and Eastern Hajar Mountains, including from Hatta southwards to Wadi Jizzi (G.R. Feulner in litt, MEW 2010).
Assessed status
Asessment status in full
Endangered
Assessment status abreviation
EN
Assessment status criteria
B1ab(iii)+2ab(iii)
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 near-endemic to the UAE, with a global distribution restricted to the Hajar Mountain chain in the UAE and Oman. In the UAE, it is found in the Hajar Mountains, where it is known from four locations. Two specimens are known from the Wadi Wurayah National park (WWNP) area: a historical record from the upper Wadi Siji in the WWNP buffer zone, and one from the upper Wadi Zikt (Feulner 2016). <a href=""http://data.rbge.org.uk/herb/E00181462"">RBGE Herbarium</a> hold one specimen from five kilometers southeast of Masafi, below Jebel Masafi. A further record is known from Wadi Hatta and Jebel Hatta. Both the EOO (&lt;100 km<sup>2</sup>) and the AOO (&lt;100 km<sup>2</sup>) are highly restricted. Grazing by livestock and feral animals (donkeys, goats) is likely to impact the species and its habitat, and the number of mature individuals is suspected to be fewer than 1,000. The species is assessed as Endangered (EN B1ab(iii)+2ab(iii)) as a result of its restricted extent of occurrence (AOO) and area of occupancy (AOO). No rescue effect is applied.
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
Near_endemic
Endemism Notes
Is an endemic?: Near_endemic
Endemism specifics: This species is near-endemic to the UAE
Conservation
Threats listed in assessment
Grazing by livestock and feral animals (donkeys, goats) is likely to impact the species and its habitat.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
The same situation is assumed.
Verified entry
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Lindenbergia 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 species is found in the drought-deciduous thorn woodland and open xeromorphic shrubland on alluvial lowland (Euphorbia larica-Acacia tortilis community), on wadi banks, in rock fissures and on rocky hill slopes (Patzelt 2014). It is usually a sparse, erect, opposite-leafed shrub, typically found on the vertical wadi walls of coarse gravel terraces in the UAE (Feulner 2016). Its altitudinal range is 20-600 m (Patzelt 2014).
Taxon
Taxa
Lindenbergia arabica | (S.Moore) Hartl
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
Within the UAE, the species is restricted to the Hajar Mountains (Jongbloed et al. 2003). The species is found in small number in Wadi Wurayah National Park (scattered locations in the lower Waterfall Wadi, lower tributary of Wadi Ghayl, and the upper Wadi Siji, with a single historical record from Wadi Zikt; Feulner 2016) but it is absent from the Ru'us al-Jibal (Feulner 2011). This species is endemic to the Hajar Mountains in the UAE and northern Oman (Patzelt 2014).
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 relatively widespread in northeastern parts of the UAE and 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
No
Endemism Notes
Is an endemic?: No
Endemism specifics: This species is endemic to the Hajar Mountains in the UAE and northern Oman
Conservation
Threats listed in assessment
This species appears to be under no immediate significant threat. The population structure, and plants, are generally small but healthy (Patzelt 2014). Grazing by livestock and feral animals may impact the species in parts of its range.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Launaea omanensis | 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 has leafless stems that originate from a rosette of leaves on the ground, in addition to a daisy-like flower (Feulner 2016). The Wadi Wurayah National Park records were found in a small scree gully at Ghalil al-Haban, the others in tributary wadis of Wadi Ghayl: one in wadi bed of third order tributary, two flowering in shallow gullies on terraces (Feulner 2016). It is also found on gravel slopes.
Taxon
Taxa
Launaea omanensis | N.Kilian
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
Within the UAE, the species has been recently recorded from four widely-spaced localities within Wadi Wurayah National Park (WWNP; Feulner 2016, Judas 2016). Feulner (2016) also notes a record from the 'Olive Highlands', on a rocky ridge on the slopes of Jebel Qitab southwest of Fujairah city, in Fujairah Emirate. The species is considered endemic to the Hajar Mountains which span Oman and the UAE (Feulner 2011). Despite the few records shown here, it is likely to be more widespread, and it is hard to identify when not in flower.
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 has been recorded within the Wadi Wurayah National Park and in the 'Olive Highlands' area of the Hajar Mountains within the UAE. It was originally considered to be endemic to Oman, but it is now known to be endemic to the Northern Hajar Mountains of Oman and the UAE. Due to being a fairly new record, there is little information available on this species within the UAE, and it is known from very few specimens and observations. However, the population size is suspected to be low. The species could be given a precautionary assessment of Near Threatened on the basis of an assumed restricted population size, and probably susceptibility to grazing. However, populations in adjacent parts of Oman are found in moister areas and are likely to be in good status. Therefore, a regional adjustment of one category is applied, so it is instead listed 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
No
Endemism Notes
Is an endemic?: No
Endemism specifics: The species is considered endemic to the Hajar Mountains which span Oman and the UAE
Conservation
Threats listed in assessment
Grazing by livestock may impact the species in parts of its range.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off