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

Imperata cylindrica | 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 locally common on sand and abandoned fields (Jongbloed et al. 2003, M. Jongbloed pers. comm. 2019).
Taxon
Taxa
Imperata cylindrica | (L.) P.Beauv.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
In the UAE, this species is known from the Hajar Mountains and from the Mazyad Oasis close to Jebel Hafeet (Jongbloed et al. 2003, M. Jongbloed pers. comm. 2019). Globally, the species occurs as a native species throughout most of Africa and around the Mediterranean basin, and has been very widely introduced across Asia and to the Americas (Board of Trustees, RBG Kew 2019). It is not listed as occurring in the UAE by Plants of the World Online, and is also considered doubtful for Oman.
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 distribution and population status of this species within the UAE is needed. 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
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

Glinus lotoides | UAE National Red List of Vascular Plants

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
In the UAE, the species was found growing in occasionally inundated areas in wet clay soils in the front of dams and 'water breakers' (Mahmoud et al. 2016). It grows as a prostrate to spreading annual or short-lived perennial, up to 0.5 m high (Mahmoud et al. 2016). The native habitat includes temporary pools with clay bottoms and the beds of temporary rivers, canal banks, and moist ground where soils are inundated in winter and dry up in early summer (El-Hamidi et al. 1967).
Taxon
Taxa
Glinus lotoides | L.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species is recently reported for the UAE, with records from Fujairah (Wadi Ham dam), Ras Al Khaimah (Wadi Al Qowr dam, Wadi Al Mansab dam, Wadi Al Mudaynah dam, Wadi Shawkah dam, Wadi Al Qasheesh dam, and Wadi Sfini dam) (Mahmoud et al. 2016). The native range is of this species is given as tropical and subtropical Old World by Plants of the World Online (Board of Trustees, RBG Kew 2019). Mahmoud et al. (2016) give the native range as Eurasia and Africa, stating that the species has become widespread in tropical, subtropical and warm-temperate areas worldwide (El-Hamidi et al. 1967). Regionally, it has been recorded in Saudi Arabia, Oman, Yemen and Socotra, as well as the UAE (Mahmoud et al. 2016).
Assessed status
Asessment status in full
Data Deficient
Assessment status abreviation
DD
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species is a recent record for the UAE, where it has been found from a number of anthropogenic dam sites (Mahmoud et al. 2016), almost all of them created since the late 1990s. The species might occur naturally in the UAE, as either a recent introduction (e.g., carried by wetland birds) or have been present but not previously identified, and it is possible that the species population and range has expanded in recent years with the increase in available habitat. The origin and distribution of this species in the UAE requires confirmation, and it is therefore assessed as Data Deficient pending this.
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

Schoenoplectus litoralis | UAE National Red List of Vascular Plants

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
In the UAE it is found in or close to standing water. This species is tufted and can grow up to 2 m in length (Ghazanfar and Fisher 1998).
Taxon
Taxa
Schoenoplectus litoralis | (Schrad.) Palla
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxonomic Notes
Schoenoplectus litoralis is based on Scripus litoralis Schrad. Scripus litoralis auct. non Schrad. in India is Schoenoplectus subulatus (Vahl) K. Lye. Both are present in India. Cook (1996) treats S. subulatus (Vahl) K. Lye in his 'Account of aquatic and wetland plants of India' but not Schoenoplectus litoralis.
Taxon distribution as listed in assessment
The species was recorded for the UAE in 1996 from an unknown locality (Böer and Eschmann-Grupe 1996), however it was long mistaken for other taxa, and it is now considered to be widespread in the mountain areas of the UAE where standing water is present. Globally, this species occurs from Africa to temperate Eurasia (Board of Trustees, RBG Kew 2019). According to Plants of the World Online, this species is not native to the UAE (Board of Trustees, RBG Kew 2019). The UAE is also not listed as a country of occurrence on the most recent Red List Assessment for this species (Mani 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
In the UAE this species is known from the Hajar Mountains. It is restricted to areas of standing water which are potentially under threat from water abstraction and declining rainfall patterns. However, it is considered Least Concern at present given its relatively wide distribution across the mountains in the UAE and regionally.
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
Declining rainfall and water abstraction may impact this species.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
Although not widely recognised in 1996 (first recorded in 1996), it is considered likely that the species was also LC at that time.
Verified entry
Off

Aeluropus lagopoides | 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 perennial herbaceous grass (Geophyte) that inhabits sandy stretches along the coastline, inland swamps and salt marshes, and also occurs in irrigated urban areas.
Taxon
Taxa
Aeluropus lagopoides | (L.) Trin. ex Thwaites
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
In the UAE, the species along central and eastern parts of the Arabian Gulf coast, including offshore islands, along the east coast, and from Jebel Hafeet (Jongbloed et al. 2003). The species also occurs in inland saline marshes (MEW 2010) and in irrigated areas within urban areas (Perry 2008). This is a Mediterraneo-Touranian (Mediterranean basin and Iran) species. It is widespread from West Africa to Central Asia and the Indian subcontinent; also found in southern parts of Europe, including Sicily, Karpathos, Crete, Cyprus and Malta.
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 in coastal parts of the UAE and is found in some inland areas. Whilst subpopulations will have undergone a significant decline as a result of coastal development, it is thought that the species still 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
The urbanization of the coastline for tourism and industrial development is the main threat to this species and its habitat.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Arundo donax | 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 or near water, in wadis and irrigated places (Jongbloed et al. 2003) and seepages (Feulner 2011). It is a perennial species with woody rhizomes that grows to 300(-600) cm and flowers from January to June (Jongbloed et al. 2003).
Taxon
Taxa
Arundo donax | L.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
The species is common and widespread in the Hajar Mountains in eastern UAE (Jongbloed et al. 2003). Feulner (2011) records the species from a single native site ('Ayn as-Sih, wadi al-'Ayn) in the Ru'us al-Jibal, however this locality is in Oman. The species is also considered native to Abu Dhabi Emirate (S. Sakkir pers. comm. 2018), but the distribution there is uncertain, and its use as an ornamental plant in Abu Dhabi city is also reported. The species is listed as an introduced plant by MoCCaE (O. Al Shamsi pers. comm. 2019) and Al Mehairbi et al. (2019). The species is considered to be native from West and Central Asia to temperate East Asia, although only the 'Gulf States' is referred to, not the UAE specifically (Board of Trustees, RBG Kew 2019). GRIN (2019) cite only Saudi Arabia in the Arabian Peninsula; the true native distribution is obscure (CABI 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
The species is common and widespread in the Hajar Mountains in the eastern UAE. Whilst almost certainly Least Concern in relation to its distribution and population size and trend, the species is considered Data Deficient given the significant uncertainty of the origin of the species 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
The species would be vulnerable to the decline in surface water, such as from long-term climate change.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Spergularia marina | 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 is an annual herb species that can be found in plantations (El-Keblawy and Abdelfatah 2014, Mahmoud et al. 2018). This plant grows up to 25 cm in height, has fleshy linear leaves and produces pink and white flowers between February and April (Jongbloed et al. 2003). It appears to prefer shaded sites but can also tolerate saline soils (Jongbloed et al. 2003). MEW (2010) gave the habitat as ""moist locations in gravel and sand"".
Taxon
Taxa
Spergularia marina | (L.) Griseb.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
Within the UAE, this species has been recorded from Abu Dhabi and Digdaga, in addition to along the Dibba to Khor Fakkan road (Jongbloed et al. 2003) and in Hatta. It is suggested to have a very localised distribution along the east coast, although G. Feulner does not know this species from this area (G. Feulner pers. comm. 2019). Its maximum EOO was initially estimated to be 2,709 km<sup>2</sup> when including a locality at Ras al-Khaimah, however, when excluding this locality (as this species presence is currently uncertain here), the EOO estimate is 812 km<sup>2</sup>. There are considered to be less than ten locations according to the major threats to this species. Its native range spans across the temperate northern hemisphere in addition to South America (Board of Trustees, RBG Kew 2019).
Assessed status
Asessment status in full
Vulnerable
Assessment status abreviation
VU
Assessment status criteria
B1ab(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 generally recorded from two localities in the UAE, although further scattered localities may also form part of its range. If these are taken into consideration, the maximum extent of occurrence (EOO) for the species is estimated be between 812-2,709 km<sup>2</sup>. In addition, Spergularia marina is experiencing ongoing decline in habitat extent and quality due to coastal development within its range, and is estimated to occur in less than ten threat-based locations. Therefore, this species is assessed as Vulnerable (VU B1ab(iii)).
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 is threatened by coastal development along the east coast of the UAE.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
There have been increasing levels of development along the East coast of the UAE since 1996, and so it is assessed as being Near Threatened in 1996, whereas now it is Vulnerable.
Verified entry
Off

Potamogeton schweinfurthii | 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 a submerged, aquatic plant and can be found in shallow pools of fresh or mildly brackish water (Ghazanfar and Fisher 1998, MEW 2010). There is little other information available regarding its habitat and ecology in the UAE.
Taxon
Taxa
Potamogeton schweinfurthii | A.Benn.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxonomic Notes
Potamogeton schweinfurthii is closely related to P. lucens and P. illinoensis.
Taxon distribution as listed in assessment
The origin and distribution of this species in the UAE requires confirmation. The species is only listed, without details, in Jongbloed et al. (2003), while G.R. Feulner (in lit. MEW 2010) comments that the species is not found in natural wetland sites (e.g. wadi pools) in the UAE, only in dam reservoirs, scrapes, and in artificial ponds. Globally, this species is native to Africa, the Mediterranean, the Arabian Peninsula and Iran (Board of Trustees, RBG Kew 2019). Whilst Plants of the World Online includes the UAE in the global distribution of the species, the current global assessment of this species excludes the UAE, only including Yemen within the Arabian Peninsula.
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 regarding the origin and distribution of this species within the UAE. As such, it is difficult to accurately assess this species, and it is therefore 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

Najas marina | 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 known sites within the UAE are within water storage reservoirs and dams. The submerged aquatic plant species grows in pools and slow-flowing freshwater streams, although often in brackish water (Jongbloed et al. 2003, Ghazanfar and Fisher 1998, Wood 1997, Miller and Morris 1988). The leaves are linear to oblong in shape and grow in pseudo-whorls (Ghazanfar and Fisher 1998). This species is known to be dispersed by birds and is also eaten by camels in Oman (S. Ghazanfar pers. comm. 2019).
Taxon
Taxa
Najas marina | L.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxonomic Notes
Numerous subspecies have been described within this species (Triest 1988) but these are not consistently recognised.
Taxon distribution as listed in assessment
Within the UAE, it has been recorded from the dam at Khor Fakkan, in the Emirate of Fujairah (Böer and Chaudhary 1999). It is also known from dams in Hatta and Al Manama. In the Arabian Peninsula, it occurs in other countries including Saudi Arabia (Chaudhary 2001), Oman (Miller and Morris 1988), Yemen (Wood 1997) and Socotra (Miller and Morris 2004), however, the draft Red List assessment of this species for the Arabian Peninsula (A. Patzelt and S.G. Knees) does not list the UAE in its distribution, and the origin of the species in the UAE requires confirmation, given its occurrence in anthropogenic sites. Globally, this species is widespread across cosmopolitan areas of North and South America, Europe, Asia, Africa and Australasia (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
Within the UAE, the species has been recorded from dam and water storage sites in the north-east of the UAE (Böer and Chaudhary 1999). Whilst it is known from other countries in the Arabian Peninsula, the draft Red List assessment of this species for the Arabian Peninsula (A. Patzelt and S.G. Knees) does not list the UAE in its distribution, and the origin of the species in the UAE requires confirmation, given its presence at anthropogenic sites. In addition, there is no information on population size or trend and the continued presence of the species at the known sites, as well as occurrence elsewhere in the country, requires further research. As a result, the species 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
This species does not appear to be subject to any major threats.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Bolboschoenus maritimus | 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 plant, with underground tubers, found in swampy ground near freshwater (Jongbloed et al. 2003). It may also be found in anthropogenic habitats.
Taxon
Taxa
Bolboschoenus maritimus | (L.) Palla
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxonomic Notes
Until recently, other taxa were included within the concept of B. maritimus; this obscures the limits of its distribution and may obscure population trends.
Taxon distribution as listed in assessment
Within the UAE, Jongbloed et al. (2003) reported this species from a small number of scattered locations in the eastern UAE (Abu Dhabi, Al Ain, Ras al Khaimah). Survey data from the Sharjah Seedbank & Herbarium show additional scattered records (Hatta, coastal Ras al-Khaimah and eastern Sharjah). Feulner (2016) reported this species from Wadi Wurayah National Park (pools at the base of the Wadi Wurayah waterfall and along the wadi above), an area that is intensively used by tourists; the origin of the species here requires confirmation. The species has an enormous global distribution in temperate and subtropical regions (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 reported from a small number of scattered locations in the eastern UAE (Abu Dhabi, Al Ain, Ras al Khaimah, Sharjah, Hajar Mountains). However, the identification of B. maritimus and B. glaucus is difficult, and B. maritimus is easily confused with other wetland sedges found in the UAE. As a result, it is not certain whether the species found in the UAE is B. maritimus or B. glaucus. In addition to this uncertainty, the coastal wetlands habitats of these Bolboschoenus species have undergone significant change due to development, water abstraction, climate change and pollution. Further research is required to confirm the presence and distribution of this species in the UAE and, therefore, it is considered Data Deficient.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
The likely threats to this species include development, surface and groundwater abstraction, pollution, and reduced rainfall through climate change.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Crassula alata | 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 known to be found in mountains at moderate altitudes.
Taxon
Taxa
Crassula alata | (Viv.) A.Berger
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species was first described for the UAE (Wadi Bih, Ras Al Khaimah) in 1999 (Böer and Chaudhary 1999) but a specimen was actually collected earlier, in 1980 (<a href=""http://data.rbge.org.uk/herb/E00361435"">RBG Edinburgh Herbarium</a>: ""Jabal Ruwaydah, at head of Wadi Sidakh; north-facing limestone hillside, 500 m""). The native range is Greece, the southern and eastern Mediterranean, through the Arabian Peninsula, to southern central China (Board of Trustees, RBG Kew 2019).
Assessed status
Asessment status in full
Data Deficient
Assessment status abreviation
DD
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species is known in the UAE from one confirmed record in 1980 from Jebel Ruwaydah in the southern Ru'us al-Jibal of the UAE, and from one later record from Wadi Bih (also Ru'us al-Jibal). Nothing is known of the population size and trend, and confirmation of the distribution and population status of this species is needed. Therefore, the species is considered Data Deficient.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
Without detailed information on the distribution in the UAE, little can be said about threats, however, as a Palaearctic species on the periphery of its range, it may be susceptible to climate change.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off