NT
Assessment ID
330276
Taxon name
Koelpinia linearis
Uploaded by
National Red List Database
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330270
Taxon name
Calendula arvensis
Uploaded by
National Red List Database
Scientific name
Calendula arvensis
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
magnoliopsida
Order
asterales
Family
asteraceae
Genus
Calendula
Species
arvensis
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
A2a
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species, although being described as 'not common' or 'occasional', is considered to be a weed in certain habitats. The species is known to have declined over time as a result of changing rainfall patterns. It is known to survive within both disturbed areas and at a wide range of altitudes. The species is Near Threatened because of a population decline (approaching 30%) over the last ten years.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species is widespread in the Hajar Mountains and Ru'us al-Jibal (Jongbloed et al. 2003). This plant species can be found in silt and fallow fields up to 1,200 m and above (Feulner 2011). However, it is also recorded at lower elevations within montane areas too (Feulner 2011). The global distribution of this species is in Macaronesia, Europe to the Mediterranean and West Himalaya, and the Arabian Peninsula (Board of Trustees, RBG Kew 2019).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This is an annual herb species which produces yellow flowers from January to March (Jongbloed et al. 2003, Norton et al. 2009). It grows to heights of up to 30 cm and typically occurs in silt substrate between rocks in montane areas (Jongbloed et al. 2003). This species can be found in sandy and gravelly habitats, wadis, plantations and fallow fields (MEW 2010, Feulner 2011). It is sometimes considered as a weed of disturbed areas and silty depressions within its habitat (Norton et al. 2009). It is highly rain-dependent.
Threats listed in assessment
Grazing by goats may affect this species in parts of its range (Shahid 2017). Declining rainfall is thought also be causing declines.
History
This species is considered to have become much less common due to decreasing frequency of wet years. In addition, increasing grazing may have contributed to population declines since 1996.
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330129
Taxon name
Avicennia marina
Uploaded by
National Red List Database
Scientific name
Avicennia marina
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
magnoliopsida
Order
lamiales
Family
acanthaceae
Genus
Avicennia
Species
marina
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
B2ab(iii)
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species is assessed as Near Threatened due to its restricted distribution. The AOO is estimated at close to 150 km<sup>2</sup> and there is still ongoing development of coastal areas within the UAE, however, the number of threat-based locations is estimated to be greater than 10. Although this species represents the dominant mangrove species and the area of mangrove habitat has actually increased in the UAE within the last 10-20 years, mangroves are still at risk from intensive coastal development. In addition, these trees have important economic and ecological value in terms of providing habitats to other species and tolerating extreme conditions. It is recommended that more of these habitats are designated as protected areas, along with ongoing planting strategies.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species occurs across the coast of Abu Dhabi and other areas of the UAE, including off-shore islands (Sakkir et al. 2017). The distribution consists of discontinuous patches along the coastline which is likely the result of coastal development (Sakkir et al. 2017). Within Abu Dhabi alone, this species is estimated to cover an area of 40 km<sup>2 </sup>(Saenger et al. 2004). Throughout the UAE as a whole, there are considered to be 60-70 km<sup>2</sup> of natural mangroves, and slightly over 150 km<sup>2</sup> of mangroves when including planted individuals (EAD 2014, H.S. Das pers. comm. 2019). The number of threat-based locations for this species is estimated to be greater than 10 due to multiple patches existing along the UAE coastlines. Its native range extends across the tropical and subtropical Old World (Board of Trustees, RBG Kew 2019).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This mangrove species typically along the coast of the UAE in estuaries, sheltered bays and creeks (Norton et al. 2009, Beech 2009). It is characteristic of the tidal zone, muddy inlets estuaries and shallow lagoons (Patzelt 2015). Avicennia marina is currently the only species of mangrove to grow naturally within the Arabian Gulf (Böer and Saenger 2006, Zander and Bruckner 2005). It is highly tolerant towards high temperatures in addition to salinity (Beech 2009) and has been described as a 'notoriously tolerant' species (Feulner 2000). However, this species shows increased growth in lower salinity levels (Llewellyn-Smith 2011). Individual trees have been recorded to grow up to 8 m in height, but typically grow to around 4-5 m (Aspinall et al. 1995, Perry 2008). The mangrove flowers between May and June and begins to bear its almond shaped, pale green fruit from September (Jongbloed et al. 2003, Saenger et al. 2002). Holes in the trees of this species provide a home for kingfishers, Limonium axillare (Aspinall et al. 1995). They are also associated with the macrophytic green algae genus Enteromorpha (Ghazanfar and Fisher 1998). It also provides habitats for fish and crustaceans, in addition to breeding habitats for other species of bird (Perry 2008).
Threats listed in assessment
Mangrove habitats used to be much more widespread in the UAE than they are currently (Hogarth and Beech 2001). These populations were depleted through using the wood of the trees for architecture and for building boats (Hogarth and Beech 2001). These trees are grazed by camels which can reduce their overall height (Karim and Dakheel 2006), however this is not thought to be a major threat as these trees are not though to be very palatable to animals (Norton et al. 2009). Expansion of coastal areas for public recreation will threaten this species as the coastline is converted from natural habitats (Ghazanfar and Fisher 1998). Losses in mangrove habitat area from several of the Emirates have been noted in the past two decades, due to land use change and development (Moore et al. 2013). In addition, physical removal of mangroves and hydrological changes to these coastal areas as a result of creation of new islands are important threats to the grey mangrove (H.S. Das pers. comm. 2019). However, despite this potential threat, it appears that over the last 10-20 years the UAE's extent of mangrove habitats seems to have actually increased, overall (Moore et al. 2013).
History
This species is still impacted in parts of its rage from coastal development, however, conservation efforts and planting regimes have helped to increase the area occupied by this species in the UAE, in addition to facilitating an overall population increase within the species' historical range.
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330108
Taxon name
Halophila stipulacea
Uploaded by
National Red List Database
Scientific name
Halophila stipulacea
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
liliopsida
Order
alismatales
Family
hydrocharitaceae
Genus
Halophila
Species
stipulacea
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
B2ab(iii)
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This seagrass species occurs along the Arabian Gulf coastline of the UAE, in Abu Dhabi, Dubai and Ras al-Khaimah. The estimated AOO is under 2,000 km<sup>2</sup> and there are considered to be more than ten threat-based locations. Halophila stipulacea is currently undergoing a decline in the extent and quality of its habitat due to multiple threats including oil-related activities, pollution, dredging, coastal development and fishing culture. Therefore, this species is assessed as Near Threatened.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Within the UAE, this species is known to occur along the Arabian Gulf coast (Phillips et al. 2002). The maximum AOO of this species is estimated to be under 2,000 km<sup>2</sup>, incorporating the area of this species found in Abu Dhabi and Ras al-Khaimah (H.S. Das pers. comm. 2019). Due to the occurrence of multiple seagrass meadows along the UAE coastline, there are estimated to be greater than ten threat-based locations. The native range of this species encompasses Egypt to India and the West Indian Ocean (Board of Trustees, RBG Kew 2019).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This perennial herb is a seagrass species (Norton et al. 2009, Phillips et al. 2002). It can grow at depths between 2-8 m (H.S. Das pers. comm. 2019).
Threats listed in assessment
This species is particularly susceptible to coastal development but can recover quickly if disturbance ceases and conditions improve. It can also be affected by siltation and sedimentation (Short et al. 2010, Erftemeijer and Shuail 2012). In the UAE, the species is impacted by coastal dredging and land reclamation and development, fish trawling activities, oil spills and oil pollution, oil extraction developments, coastal water eutrophication and salinisation (from water desalination plants), siltation, and other forms of pollution (Erftemeijer and Shuail 2012). Given its shallow water habitat, this species may also be threatened by climate change and the associated increase in storm activity, water temperature, and/or sea-level rise (Short et al. 2010).
History
Coastal development within the UAE has been increasing in frequency and intensity since 1996, reducing the extent and quality of available habitat for this species.
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330083
Taxon name
Halophila ovalis
Uploaded by
National Red List Database
Scientific name
Halophila ovalis
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
liliopsida
Order
alismatales
Family
hydrocharitaceae
Genus
Halophila
Species
ovalis
Taxonomic notes and synonyms listed
This a member of the Halophila ovalis complex, which is under taxonomic review. Historically, other species currently considered to be in this complex may have been labelled as H. ovalis.
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
B2ab(iii)
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This seagrass species can be found along the coastlines of Abu Dhabi and Dubai. The estimated AOO is around 3,000 km<sup>2</sup> and it is considered to occur at more than ten threat-based locations. Halophila ovalis is experiencing a continuing decline in the extent and quality of its habitat due to multiple threats, such as dredging of coastlines for artificial island creation, oil related activities, pollution and climate change. Therefore, this species is assessed as Near Threatened.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Within the UAE, the species is known to occur in Abu Dhabi Emirate (Phillips et al. 2002) in addition to Dubai. The AOO of this species is estimated to be around 3,000 km<sup>2</sup> (H.S. Das pers. comm. 2019). The number of threat-based locations is estimated to be greater than ten, due to the multiple patches of seagrass found along the UAE coastline. The native range of this species spans from the Red Sea area to Madagascar and on to the Pacific (Board of Trustees, RBG Kew 2019).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This plant is a species of seagrass (Phillips et al. 2002). It can grow at depths of up to 14 m (H.S. Das pers. comm. 2019).
Threats listed in assessment
This species is particularly susceptible to coastal development but can recover quickly if disturbance ceases and conditions improve. It can also be affected by siltation and sedimentation (Short et al. 2010, Erftemeijer and Shuail 2012). In the UAE, the species is impacted by coastal dredging and land reclamation and development, fish trawling activities, oil spills and oil pollution, oil extraction developments, coastal water eutrophication and salinisation (from water desalination plants), siltation, and other forms of pollution (Erftemeijer and Shuail 2012). Given its shallow water habitat, this species may also be threatened by climate change and the associated increase in storm activity, water temperature, and/or sea-level rise (Short et al. 2010).
History
Coastal development within the UAE has been increasing in frequency and intensity since 1996, reducing the extent and quality of available habitat for this species.
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330035
Taxon name
Eleocharis geniculata
Uploaded by
National Red List Database
Scientific name
Eleocharis geniculata
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
liliopsida
Order
poales
Family
cyperaceae
Genus
Eleocharis
Species
geniculata
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
B1ab(iii,v)
Criteria system used
IUCN
(see Assessment details)
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.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
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.
Endemic to region
Not assigned
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).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
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).
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).
History
The species is assessed as Least Concern in 1996, as it was much more common at the time.
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330018
Taxon name
Ophioglossum polyphyllum
Uploaded by
National Red List Database
Scientific name
Ophioglossum polyphyllum
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Ferns and Allies
Kingdom
Plantae
Phylum
tracheophyta
Class
polypodiopsida
Order
ophioglossales
Family
ophioglossaceae
Genus
Ophioglossum
Species
polyphyllum
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
B1b(iii)
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species occurs within sand and coastal habitats in the UAE and has an estimated extent of occurrence of 2,646 km<sup>2</sup>; this falls within the threshold for Endangered under Criterion B. In addition, the species' habitat is declining due to ongoing coastal development, causing the once common species to become less common in its range. However, the number of locations for this species (based on the most plausible threat of habitat degradation) is currently unclear. Therefore, it is currently assessed as Near Threatened.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This plant occurs in coastal areas and in the Hajar Mountains (Jongbloed et al. 2003) and has been found to occur in Wadi Wurayah National Park, Fujairah (Feulner 2016). It also occurs at Jebel Ali along the Arabian Gulf Coast. The estimated EOO of this species is 2,646 km<sup>2</sup>. Globally, Ophioglossum polyphyllum is distributed across Africa and southwest Asia, eastwards to India and southwards to South Africa (Board of Trustees, RGB Kew 2018). In Europe it occurs only on the Canary Islands (Christenhusz et al. 2017). It is also distributed in Central America and Australia (Board of Trustees, RGB Kew 2018).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This perennial fern species is known to grow in open sand habitats and coastal areas (Jongbloed et al. 2003, Rothfels et al. 2012). At higher altitudes, it can grow within silt rather than sand (Jongbloed et al. 2003). It has two or three elliptic leaves growing from the stem in addition to other stem like leaves (Jongbloed et al. 2003). The plant generally appears after periods of rain (Jongbloed et al. 2003).
Threats listed in assessment
This plant is reportedly threatened by development in its coastal habitat range (Jongbloed et al. 2003, Feulner 2016).
History
Coastal development within the UAE has been increasing in frequency and intensity since 1996, reducing the extent and quality of available habitat for this species.
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330607
Taxon name
Butorides striata
Uploaded by
National Red List Database
Scientific name
Butorides striata
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
pelecaniformes
Family
ardeidae
Genus
Butorides
Species
striata
Taxonomic notes and synonyms listed
Butorides striata;(del Hoyo and Collar 2014) was previously split as;B. striata;and;B. virescens;following AOU (2003), and before then;B. striata;was split as;B. striatus;and;B. sundevalli;following Sibley and Monroe (1990, 1993). Gender agreement of;B. striata;follows David and Gosselin (2002).
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
D1
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a restricted resident population in the UAE, which might qualify it for listing as Vulnerable. However, the population is increasing, and the potential for immigration from outside the UAE remains very high, as the breeding population in the wider Arabian Peninsula is likewise increasing. Therefore, the species's status has been adjusted down to Near Threatened at the national level.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species is a common resident along both coasts of the UAE, but uncommon to rare further inland (Pedersen et al. 2017).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This species is mainly coastal. It favours mangrove habitats, but is also found along rocky and sandy coasts, coral reefs, harbours, breakwaters and jetties (Richardson 1990, Jennings 2010, Aspinall and Porter 2011). It is occasionally found at inland wetlands, including water-filled rubbish dumps, sewage treatment plants and gravel pits (Richardson 1990). The species forages mainly in stands of Black Mangroves Avicennia marina. In Arabia, it has only been observed to feed on fish, but elsewhere it also takes crabs, shrimps and other invertebrates (Jennings 2010). The breeding period lasts over spring and summer; the species may be double-brooded. Nests are loose structures of sticks and algae, which are hidden in bushes or rock crevices. The clutch size is not known; evidence from the Red Sea suggest that clutches contain four eggs (Jennings 2010).
Threats listed in assessment
The most pertinent threats to this species are from habitat destruction (e.g. the loss of mangroves) (Aspinall 1996, Kushlan and Hancock 2005), and pollution (e.g. from oil) (Aspinall 1996).
History
The species was much less common in 1996, qualifying as Endangered, adjusted by one step to VU. The population increases for this species are likely a result of increased availability of artificial water sources.
Publication
Burfield, I.J., Westrip, J., Sheldon, R.D., Hermes, C., Wheatley, H., Smith, D., Harding, K.A. Allen, D.J. and Alshamsi, O. 2021. UAE National Red List of Birds. Ministry of Climate Change and Environment, Dubai, United Arab Emirates
Assessment ID
330587
Taxon name
Alaemon alaudipes
Uploaded by
National Red List Database
Scientific name
Alaemon alaudipes
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
alaudidae
Genus
Alaemon
Species
alaudipes
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
C2a(ii)
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a small population size within the UAE, which is suspected to be in decline as a result of ongoing threats. As such it is assessed here as Near Threatened under criterion C2a(ii).
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species is a fairly common resident in the UAE. It is distributed across the entire country (Pedersen et al. 2017).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This species is especially common on desert plains, but is generally found in a wide variety of flat habitats, including sandy and gravel desert, semi-desert and coastal dunes (Jennings 2010, Aspinall and Porter 2011). Even though it is a shy species, it is frequently found in proximity to humans, e.g. in the outskirts of towns, in farmland and along the beach (Jennings 2010). The species is able to tolerate the hot and arid conditions of the sandy desert, and shows a variety of behavioural adaptations to combat the extreme heat, like standing in the shade, hiding in the holes of Spiny-tailed Lizards Uromastyx microlepis, or lying on shaded, damp ground (Jennings 2010). It feeds on invertebrates, which it obtains by digging in soft soil, chasing and aerial pursuits, or by searching in rock crevices. Occasionally, it takes small invertebrates like lizards (Jennings 2010). The species is territorial throughout the year. The breeding season lasts from February to July or even October, depending on the amount of rainfall (de Juana and Suárez 2019). The courtship display of the males include frequent calls with rising and falling notes, which consist of trilled whistles and clicks (S. Alam (Dubai Municipality) pers. comm. 2019). Males also perform distraction displays when the nest or chicks are threatened (S. Alam (Dubai Municipality) pers. comm. 2019). The nest consists of a cup dug into the ground, often in open conditions and exposed to the sun. Nests observed in the Dubai desert were located in bushes of Zygophyllum hamiense and made of soft twigs and lined with fine grass and feathers (S. Alam (Dubai Municipality) pers. comm. 2019). Clutches contain two eggs; both sexes take turns in incubating and rearing the young (S. Alam (Dubai Municipality) pers. comm. 2019)
Threats listed in assessment
Changes to land-use (particularly the planting of trees) in desert areas can have local effects on this species (Aspinall 1996), and the species is also negatively impacted by urban development, and the expansion of agriculture. A high rate of nest failure has been recorded, either due to trampling by goats and humans, depredation or overwhelming by drifting sand (Jennings 2010). Off-road driving and the failure of rainfall may also be having a negative impact (S. Alam in litt. 2019).; Overgrazing outside of Protected Areas could also be an issue.
History
This species is assessed here as Near Threatened under criterion C2a(ii), as it is suspected that its relatively small population size is undergoing a decline. As key threats such as urban and agricultural expansion likely had minimal impacts on the species in 1996, the backcast assessment for then is considered here to be Least Concern.
Publication
Burfield, I.J., Westrip, J., Sheldon, R.D., Hermes, C., Wheatley, H., Smith, D., Harding, K.A. Allen, D.J. and Alshamsi, O. 2021. UAE National Red List of Birds. Ministry of Climate Change and Environment, Dubai, United Arab Emirates
Assessment ID
330583
Taxon name
Curruca mystacea
Uploaded by
National Red List Database
Scientific name
Curruca mystacea
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
sylviidae
Genus
Curruca
Species
mystacea
Taxonomic notes and synonyms listed
Previously placed in Sylvia;(del Hoyo and Collar 2016) but moved to current genus following Cai et al. (2019). Geographical variation at least partly clinal; nominate subspecies grades into turcmenica in N Iran, but evidence for intergradation otherwise scant or not conclusive. Three subspecies recognized.
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
D1
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The small non-breeding population size of this species in the UAE means that the species triggers the threshold for Vulnerable under Criterion D1. However, with conditions not deemed to be deteriorating significantly, and there being a good likelihood for a rescue effect for this population, a regional adjustment has been made. The species is, therefore, listed as Near Threatened under Criterion D1 instead.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species is common in the UAE during migration to and from the breeding grounds. Numbers are highest between late September and May (Pedersen et al. 2017). Individuals migrating through or wintering in the UAE breed from Turkey to Kazakhstan.
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This species inhabits sparsely wooded areas and broken country, like woodland, areas of scattered trees, riparian forests, thorn scrubs and thickets, cuttings, parks and gardens (Richardson 1990, Aspinall and Porter 2011). There is no information available about its diet in the UAE; elsewhere it feeds mainly on small arthropods, especially insects and their larvae and eggs, but also takes various berries, fruits and seeds (Aymí and Gargallo 2015). The species is migratory; it breeds in south-western Eurasia and winters from north-east Africa to Arabia and southern Iran (Snow and Perrins 1998).
Threats listed in assessment
There are not thought to be any current significant threats to this species, however, overgrazing outside of Protected Areas may have an impact on this species.
History
This species has increased its population size since 1996 due to increasing availability of suitable habitat, and it is suspected that the population size (accounting for regional adjustments) may have been sufficiently small in 1996 that it would have warranted a listing as Vulnerable under criterion D1 then, whereas now (2019) it is assessed as Near Threatened.
Publication
Burfield, I.J., Westrip, J., Sheldon, R.D., Hermes, C., Wheatley, H., Smith, D., Harding, K.A. Allen, D.J. and Alshamsi, O. 2021. UAE National Red List of Birds. Ministry of Climate Change and Environment, Dubai, United Arab Emirates
