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

Aeluropus littoralis | 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
Böer and Chaudhary (1999) reported this halophytic species from coastal saline flats. It is also known to occur in plantations habitats and generally appears to grow in slightly saline soils. Across its Mediterranean range, this species occurs on sandy stretches along the coastline, swamps and inland salty soils. This species has been considered as a 'weed' in the past.
Taxon
Taxa
Aeluropus littoralis | (Gouan) Parl.
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 in coastal areas (Jongbloed et al. 2003), with the first record from Ras al-Khaimah beach (Böer and Chaudhary 1999). Brown and Sakkir (2004) report the species from Abu Dhabi Emirate, without details, and it is also known from plantations along the Fujairah coast. This is a circum-Mediterranean species, with a very wide biogeographical distribution that covers southern Europe, western Asia, North Africa and extends from the Arabian Peninsula to India (Euro+Med Plantbase 2006-2010). In the Mediterranean region it is very widespread, occurring in Spain, the Balearic Islands, France, Italy, Sicily, Sardinia, Croatia, former Yugoslavia, Albania, Greece (including Crete and the East Aegean Islands), Bulgaria, Turkey, Cyprus, Syria, Lebanon, Israel, Palestine, Jordan, Morocco, Algeria, Tunisia, Libya and Egypt.
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 able to survive in saline environments and makes use of plantation habitats. It is relatively widespread and common in the UAE, occurring along the east coast in Fujairah, in addition to Ras al-Khaimah and Abu Dhabi Emirate. 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
Without detailed information on the distribution in the UAE, little can be said about threats, however, it is likely to have been impacted by coastal development.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Polypogon monspeliensis | 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 grass standing up to 1.0 m and flowering between February and May (Jongbloed et al. 2003). In the UAE it has been found to grow in gardens, plantations, along irrigation channels, and in other anthropogenic habitats. It also prefers shady and damp locations (Jongbloed et al. 2003). MEW (2010) have habitat types as ""plantations, gardens; moist and irrigated places"". Globally, this species has been known to be found in temporary pools, marshes, depressions flooded in winter, inundated plains, river estuaries, rice paddies, along stream edges, ditches and humid habitats and is considered a weed in many agricultural crops (Akhani 2014).
Taxon
Taxa
Polypogon monspeliensis | (L.) Desf.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species occurs along both the western and eastern coastal areas of the UAE (Jongbloed et al. 2003, Al Meharibi et al. 2019) and in the Hajar Mountains (Feulner 2011). Western (1983) reported the species from across Abu Dhabi Island; Western found it in the outfall of a sewage treatment works, so it may persist in anthropogenic habitats, and presence on the island is shown by Al Meharibi et al. (2019). Globally this species occurs in North and East Africa, southern Europe north to the UK, around the Mediterranean basin, to Central and East Asia. It has been introduced to the Americas, southern Africa and to Oceania (Board of Trustees, RBG Kew 2018).
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species is widespread in the UAE. Whilst subpopulations may 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
Grazing by livestock may impact the species in parts of its range, and impacts from coastal development are likely to have been significant.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Sphenopus divaricatus | 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 an annual grass with purplish stems, growing up to 0.3 m. It grows in sand and in silt between rocks (Jongbloed et al. 2003).
Taxon
Taxa
Sphenopus divaricatus | (Gouan) Rchb.
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 Sweihan and Al Khazna areas, and the Hajar Mountains (Jongbloed et al. 2003, Al Mehairbi et al. 2019). The species has also been recorded from the Dubai Creek area (Sharjah Seedbank and Herbarium), where it is possibly introduced. The EOO, based on the Sweihan and the Hajar Mountains records, is 4,300 km<sup>2</sup>. Globally this species occurs from Macaronesia, across North Africa and southern Europe, to the Middle East, Central Asia and Pakistan (Board of Trustees, RBG Kew 2018).
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
Although considered to be ""rare"" and with a restricted extent of occurrence (4,300 km<sup>2</sup>), it is unlikely that there is a continuing decline in EOO or habitat area or extent, at least in the Hajar Mountains, and the species occurs in many more than ten locations. 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
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

Potamogeton nodosus | 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
Potamogeton species are typically found in fresh and brackish water bodies (Ghazanfar and Fisher 1998). P. nodosus in particular is specifically found in deep pools and has both submerged and floating leaves (Ghazanfar and Fisher 1998).
Taxon
Taxa
Potamogeton nodosus | Poir.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxonomic Notes
Potamogeton nodosus is one of the most polymorphic Potamogeton species, showing several distinct morphotypes as well as an extreme phenotypic plasticity throughout its range. It seems likely that there has been some confusion about the distinction between this specie and others such as P. linguatus, P. ferrugineus, P. tepperi and P. sulcatus (Wiegleb and Kaplan 1998), to the extent that this evaluation could include information on some of all of those taxa. Potamogeton nodosus has been shown to hybridise with P. natans (P. xschreberi G. Fisch.), the hybrid is not common and is unlikely to affect the survival of the species or this evaluation.
Taxon distribution as listed in assessment
The species was listed without detail for the UAE by Jongbloed et al. (2003). The first record found for the species in the country dates from 1857 (<a href=""https://herbarium.univie.ac.at/database/detail.php?ID=162724"">Herbarium, Institute of Botany, University of Vienna</a>). There are no detailed distribution data available for this species within the UAE. Globally, the native range of this species spans across the Americas, European continent, Africa, temperate and tropical Asia in addition to 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
The origin and distribution of this species with the UAE appears to be unclear and there are no recent records available. Therefore, this species is currently 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

Eleocharis geniculata | 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 an annual or short-lived perennial species, up to 0.35 m (Jongbloed et al. 2003). It is usually found in moist banks of ponds and wadis (Jongbloed et al. 2003). Brackish marshes and edges of mangrove swamps are typical habitats for this species (Board of Trustees, RBG Kew 2018).
Taxon
Taxa
Eleocharis geniculata | (L.) Roem. & Schult.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
Distribution of this species is recorded from wadis in the Hajar Mountains (Jongbloed et al. 2003, Al Mehairbi et al. 2019). Feulner (2016) did not find the species (as Eliocharis geniculata) in WWNP, but would expect it to be present. The estimated Extent of Occurrence (EOO) of this species is around 1,430 km<sup>2</sup>. Globally, this is a pantropical species (Board of Trustees, RBG Kew 2018).
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
Assessment status criteria
B1ab(iii,v)
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 a restricted extent of occurrence (EOO) within the UAE and is not considered to be common within this area. The estimated EOO for this plant is around 1,430 km<sup>2</sup>, which falls within the threshold for threatened categories. The species probably occurs in more than ten threat-based locations, but the number of locations is likely to be restricted. Water abstraction and declining rainfall as a result of climate are resulting in population declines. As a result, it is cautiously assessed as Near Threatened due to the restricted distribution within the UAE and declining populations. No regional adjustment is made as the extent of any rescue effect is not known.
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 increases in water abstraction in recent years has resulted in population declines (G.R. Feulner pers. comm. 2019).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
The species is assessed as Least Concern in 1996, as it was much more common at the time.
Verified entry
Off

Blumea bovei | 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
A perennial species, this plant produces inconspicuous grey-purple flowers between February and May (Jongbloed et al. 2003). It is generally found growing within damp wadis and in plantations (Jongbloed et al. 2003) as it depends on nearby surface water (G.R. Feulner, in lit, MEW 2010). It is essentially absent in environments, such as the Ru'us al-Jibal, which lack moisture (G.R. Feulner, in lit, MEW 2010, Feulner 2011).
Taxon
Taxa
Blumea bovei | Vatke
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
Blumea bovei has been recorded within the Hajar Mountains, where it is considered to be widespread (Jongbloed et al. 2003, MEW 2010). Globally, the native range of this species spans from the Sahara to the Arabian Peninsula and on to India (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
Although this species appears to have a limited distribution, it is considered to be locally widespread within the Hajar Mountains. This may well be due to its specific ecological requirements, specifically in terms of requiring water. As a result, it is likely to be locally common within suitable environments and persist well in these areas. 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

Typha domingensis | 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
The species occurs naturally in wadis where freshwater is present, as well as in coastal wetlands and artificial wetlands.
Taxon
Taxa
Typha domingensis | Pers.
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 restricted to the Hajar Mountains according to Jongbloed et al. (2003), but with additional records from Jebel Hafeet (Jebel Hafeet wadi; 1,240 m; Sakkir et al. 2018) and Wadi Wurayah National Park (Tourenq et al. 2009, Feulner 2011), although the latter record was from the outflow pool below the waterfall and the origin of the species here requires confirmation. The species is planted within sewage farms (MEW 2010) and Western (1982, 1983) recorded the species from the outfall of the old sewage farm on Abu Dhabi Island. The species also occurs in the Ras Al Khor Wildlife Sanctuary in Dubai. Al Meharibi et al. (2019) show presence northwards through the Hajar Mountains to the Ru'us al-Jibal, although the species is not listed as present there by Feulner (2011). Globally, this species has an almost cosmopolitan distribution, absent only from northern latitudes in North America and Europe, although Plants of the World Online does not include the UAE in its distribution (Board of Trustees, RBG Kew 2019). The native distribution of this species is uncertain because of taxonomic and identification confusions (CABI 2019), but we consider the species to probably be native to the UAE following draft Red List assessment for the Arabian Peninsula (Patzelt and Knees 2012).
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 Hajar Mountains in the UAE. Although data are lacking on the population size and trend, the species is assessed as Least Concern as it is thought unlikely that it will approach the thresholds for a threatened category.
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 susceptible to the over-abstraction of ground and surface water, however, the scope and impact of this within the range of the species in the UAE are not known. Long-term declines in rainfall as a result of climate change is likely to impact the species.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Bacopa monnieri | 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, at the edge of pools, and in moist places in plantations (Jongbloed et al. 2003). It is a prostrate perennial reaching up to 0.3 m in height (Jongbloed et al. 2003).
Taxon
Taxa
Bacopa monnieri | (L.) Wettst.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
In the UAE, the species is found in scattered, widespread localities, primarily through the Hajar Mountains, at edges of permanent water pools and in wet and moist places, such as in irrigated plantations (Jongbloed et al. 2003). The global range of this species are the tropics and subtropics (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-east 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
There is no information available.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Brachiaria eruciformis | 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
It is an annual species which occurs in sandy habitats in the UAE (MEW 2010, Kumar 2011). Globally, the species is a common weed in cultivated fields, which sometimes grows in roadsides, damp places, ditches, waste places and is also a weed of coffee plantations (Kumar 2011).
Taxon
Taxa
Brachiaria eruciformis | (Sm.) Griseb.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxonomic Notes
The species is placed as Moorochloa eruciformis (Sm.) Veldkamp by Euro+Med Plantbase (Valdés and Scholz 2009) and by Plants of the World Online (Board of Trustees, RBG Kew 2020).
Taxon distribution as listed in assessment
This species has been recorded a few times in the UAE in sandy habitats (Jongbloed et al. 2003, MEW 2010). Specifically, it is known from Masafi and Dibba, however without precise locality data Globally, Brachiaria eruciformis extends from Mediterranean Europe east through the Caucasus and Middle East to China. It occurs throughout much of Africa, South and Southeast Asia and Australia as well as the Caribbean and southern South America (Board of Trustees, RBG Kew 2019). In India it occurs in Andhra Pradesh, Assam, Bihar, Gujarat, Goa, Jammu-Kashmir, Himachal Pradesh, Karnataka, Kerala, Madhya Pradesh, Maharashtra, Orissa, Rajasthan, Tamil Nadu, Uttar Pradesh and West Bengal (Kumar 2011).
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
Although this species has been recorded occasionally, there is little information available on the current population status and trend, in addition to potential threats. Therefore, it is currently 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

Cladium mariscus | 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 plant species with sturdy rhizomes (Jongbloed et al. 2013). It a graminaceous herb that grows to c. 2 m in height, found growing c. 5 m below permanent pools, between rocks and beside a permanent waterfall (<a href=""http://data.rbge.org.uk/herb/E00647674"">RBG Edinburgh Herbarium</a>). The species requires standing water (G.R. Feulner pers. comm. 2019). The dispersal ability of the plant seeds is uncertain, but both wind dispersal and dispersal by bird are possible.
Taxon
Taxa
Cladium mariscus | (L.) Pohl
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 confirmed from a single site (small rocky pools at the base of the waterfall and adjacent rocks) in Wadi Wurayah (first reported by V. Chalmers in 2009 (Feulner 2016); <a href=""http://data.rbge.org.uk/herb/E00647674"">RBG Edinburgh Herbarium</a> specimen collected 2013). The species was also recorded by Gallacher from the Dubai Desert Conservation Reserve, however this area represents a very different habitat and altitude, and the record requires confirmation. On a global scale, the species is native to temperate Eurasia, the Americas, North Africa, Australia and to the southwest Pacific (Board of Trustees, RBG Kew 2018). In the Arabian Peninsula, this species is also known from scattered localities in Saudi Arabia (Chaudhary 2001) and from isolated springs and waterbodies in Oman (Patzelt 2014) and on Socotra (Miller and Morris 2004). The nearest confirmed locality to Wadi Wurayah is at the Jazirah oasis in Oman (Jongbloed et al. 2003, Feulner 2016), more than 100 km away.
Assessed status
Asessment status in full
Critically Endangered
Assessment status abreviation
CR
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
Within the UAE, this species is known from a single site within the Wadi Wurayah National Park, where it was found in and around small bedrock pools near the base of the permanent waterfall. The species is assessed as Critically Endangered (CR D) on the basis of the small number of mature individuals, which was estimated to number fewer than ten. The species was not re-found at the site following heavy rains in 2014, but was present later in 2019. It is not known if there is a potential rescue effect from populations outside the UAE, although the potential for this is low given the small populations in Oman and their distance from this site. Establishment of the species at other sites with suitable habitat in the UAE is possible but, to date, the species has not been found at other freshwater sites (G.R. Feulner pers. comm. 2019).
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 habitat of this species is prone to change and damage from human disturbance (MEW 2010). Feulner (2016) notes that the species locality at the base of a waterfall is vulnerable to flash floods and the species was not found during survey following heavy rain in November 2014, nor in more recent surveys (G.R. Feulner pers. comm. 2019), but was found later in 2019. Feulner (2016) notes that the waterfall area where this species is found is subject to heavy recreational use.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
The species was not recorded in the UAE in 1996 but it is possible that the species was present either in the seedbank or as underground rhizomes or, alternatively, it was simply not found or identified in surveys. We consider that it is likely to have been present but in similarly small numbers, or as propagules, and would have qualified as CR in 1996.
Verified entry
Off