VU

Mobula mobular | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
Yes
Habitat
Habitat details as listed in assessment
The Giant Devil Ray is mostly oceanic, but is also known to occur in coastal waters (Last et al. 2016). This species reaches a maximum size 520 cm disc width (DW) with males mature around 198-205 cm DW and females around 236 cm DW (Weigmann 2016, Last et al. 2016). As is the case with other members of the genus, this species is livebearing and histotrophic, with embryonic nutrition supplied from a protein- and lipid-rich histotroph from highly developed trophonemata. A single, relatively large pup is produced per litter (Compagno and Last 1999, White et al. 2006b). Intrinsically, Manta and Mobula rays have among the lowest productivity of any chondrichthyan due to their large size, low fecundity, and late age at maturity (Pardo et al. 2016). Long resting periods may account for extended reproductive cycles in mobulid species. The generation length of this species is suspected to be around 20 years, based on the Reef Manta Ray (Manta alfredi), which reaches a similar size, is 25 years (Marshall et al. 2009).
Taxon
Taxa
Mobula mobular | (Bonnaterre, 1788)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
Recent revisions of the taxonomy of genus Mobula included the decision to consider the circumglobal Spinetail Devil Ray M. japanica (Müller & Henle, 1841) a junior synonym of the Mediterranean Giant Devil Ray M. mobular (Bonnaterre, 1788), causing M. mobular to become a circumglobal species (Poortvliet et al. 2015, Hosegood et al. 2018, White et al. 2018).Notarbartolo di Sciara et al. (2020) argued that one of the traits that were used to support the differentiation between the two species, the maximum size of M. mobular purportedly in excess of 5 m disc width (DW), can be explained by past misidentifications of M. birostris, and therefore unsubstantiated. This also supports their recommendation to retain for the species the common name Spinetail Devil Ray instead of Giant Devil Ray.
Taxon distribution as listed in assessment
The Giant Devil Ray occurs throughout UAE waters. Elsewhere, it is probably circumglobal in tropical and subtropical waters (Notarbartolo di Sciara et al. 2017).
Assessed status
Asessment status in full
Vulnerable
Assessment status abreviation
VU
Assessment status criteria
A2d
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
The Giant Devil Ray occurs throughout UAE waters. This species is not targeted or valued in markets of the UAE and capture of this species is totally banned in the UAE. It is a component of the bycatch in several fisheries, but much of this catch is unreported. It is directly targeted in Sri Lanka and India, and exported to international markets, especially China where the gill plates are highly-valued. Its low productivity causes it to be susceptible to rapid population declines. It is especially susceptible to exploitation (target and bycatch) in many largely unregulated gill net, longline and trawl fisheries that operate within its range outside and surrounding UAE waters. Some management measures are now in place in the Arabian Sea region, although domestic fisheries are likely to continue. Though data specifically from the UAE are not available, individuals in the UAE are a component of a larger, interconnected and migratory population that occurs broadly in the north-western Indian Ocean. It is inferred that declines reported in the Arabian Sea region are representative of its status in the UAE. There is no information to confirm that this species is breeding in the UAE and no information confirming the likelihood of a cease in immigration from outside the region, despite ongoing threats and recorded declines. Based on recorded levels of exploitation, it is suspected to have declined by 30-50% over the past three generation lengths, or about 60 years. It is listed as Vulnerable A2d.
Criteria system
Criteria system specifics
IUCN v3.1
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
Information pertaining to threats specific to the UAE are unavailable. This species is impacted by target (for fins and their valuable meat) and bycatch fisheries that are active elsewhere in its range. Manta rays are easy to target because of their large size, slow swimming speed, aggregation behaviour and predictable habitat use.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Anthus similis | UAE National Red List of Birds

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 inhabits rocky hills, slopes and terraced fields in the highlands (Jennings 2010, Aspinall and Porter 2011). It favours areas with bushes, sparse trees and a dense vegetation cover on the ground (Jennings 2010). Its diet includes invertebrates (grasshoppers and other insects), which it takes from the ground, sometimes even by running and chasing (Jennings 2010). Within the UAE, it breeds above c. 500 m, ranging to he highest elevations (Jennings 2010). During winter, highland birds migrate to lower elevations (Jennings 2010). In general, the breeding season of this species varies across regions and the onset of breeding in the UAE remains largely unknown. It has been suggested that the species is double-brooded, with a first clutch produced at lower altitudes with juveniles hatching between October and April, and a second clutch produced subsequently after moving to higher altitudes from late March/April on (Jennings 2010). The nest is usually loosely constructed of grass and placed in a natural hollow on a hillside, concealed by a boulder or bush (Jennings 2010). There is the possibility that locally nests might be parasitised by the Common Cuckoo (Cuculus canorus), which is assumed to breed in Musandam (Oman) and maybe ranging into northern UAE (Jennings 2010).
Taxon
Taxa
Anthus similis | Jerdon, 1840
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxonomic Notes
Anthus similis and A. nyassae (del Hoyo and Collar 2016) were previously lumped as A. similis following AERC TAC (2003); Cramp and Simmons (1977-1994); Dowsett and Forbes-Watson (1993). Anthus longicaudatus is no longer recognized as a species, following del Hoyo and Collar (2016); available material in museums is an amalgam of specimens of A. vaalensis and A. similis.
Taxon distribution as listed in assessment
This species is an uncommon to fairly common resident in the northern highlands as well as in the eastern part of the UAE. Occasionally, individuals stop in the country during migration or for wintering (Pedersen et al. 2017). The occurrence of wintering individuals in the lowland plains along the coast might be of local altitudinal migrants within the country (Jennings 2010).
Assessed status
Asessment status in full
Vulnerable
Assessment status abreviation
VU
Assessment status criteria
D1
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's breeding population within the UAE is small enough to trigger a listing as Endangered under Criterion D. However, the species is likely a recipient of immigration from outside of the country which would provide a rescue effect. Therefore, the category has undergone a regional adjustment, and the species is listed here as Vulnerable under Criterion D1.
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
Development in montane areas may potentially pose a threat, as may coastal development in its wintering range. Overgrazing outside of Protected Areas potentially could also have an impact.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
It is assessed that in 1996, the national Red List status of this species would have been the same as in this assessment.
Verified entry
Off

Riparia riparia | UAE National Red List of Birds

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 occurs over open country and wetlands, including cultivations, parks or sewage treatment plants (Richardson 1990, Aspinall and Porter 2011). There is no information available about its feeding habits in the UAE; elsewhere it forages approximately 15 m above ground, feeding mainly on insects and spiders (Tucker and Heath 1994, Turner 2004). The species is migratory; it breeds between late April and August in Eurasia (Tucker and Heath 1994).
Taxon
Taxa
Riparia riparia | (Linnaeus, 1758)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxonomic Notes
Riparia riparia and R. diluta (del Hoyo and Collar 2016) were previously lumped as R. riparia following AERC TAC (2003), AOU (1998 and supplements), Cramp and Simmons;(1977-“1994), Dowsett and Forbes-Watson (1993), SACC (2005 and updates), Sibley and Monroe (1990, 1993), and Stotz et al. (1996).
Taxon distribution as listed in assessment
The majority of occurrences of this species within the UAE are likely to be of wintering birds and migrant individuals on passage to and from the breeding grounds (Pedersen et al. 2017). Numbers are highest between August to May, when it is common over open land or waterbodies (Aspinall and Porter 2011, Pedersen et al. 2017). The species has been recorded in all months though (Pedersen et al. 2017).
Assessed status
Asessment status in full
Vulnerable
Assessment status abreviation
VU
Assessment status criteria
D1
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 relatively small non-breeding population within the UAE. On average, this would appear to even out at a level that would trigger Endangered under Criterion D, although accurately estimating the population size and trend of this species is hindered by its movement habits. A regional adjustment has been applied as it is deemed likely that a rescue effect from the wider breeding population could occur. Therefore, it is listed as Vulnerable under criterion D1.
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
Outside of the country, breeding sites are generally ephemeral and can often be lost through human activities (e.g. flood control, erosion control on rivers), and this could also be true for artificial sites where the species may occur within the UAE. Globally, the use of pesticides, causing declines in prey species, may impact the species (Tucker and Heath 1994), but this is not thought to be pertinent to the UAE. In Europe, it is often dependent on artificial breeding sites such as quarries (Turner 2004), however quarry work can adversely affect breeding, though workers often take measures to prevent this. In the past, droughts in wintering areas have caused severe large-scale population declines in western Europe (Tucker and Heath 1994, Turner 2004), and so this could be a further threat to the species within UAE.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
It is assessed that in 1996, the national Red List status of this species would have been the same as in this assessment.
Verified entry
Off

Aetomylaeus nichofii | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
Yes
Habitat
Habitat details as listed in assessment
The Banded Eagle Ray is a demersal species in continental shelf inshore waters to at least 115 m depth (Last and Stevens 2009). It reaches a maximum size of 72 cm disc width (DW) with males maturing at 39-42 cm DW (Last et al. 2016). Size at maturity for females is unknown, but pregnant females have been recorded in the UAE at 54.8 cm DW (R.W. Jabado pers. comm. 06/05/2017). Females are viviparous with litters of up to four young with a size at birth of 17 cm DW (Compagno and Last 1999, Last and Stevens 2009). Nothing else is known of this species' biology. Generation length estimated at 10 years based on the generation length of the Bat Ray (Myliobatis californicus) (14.5 years) (Martin and Cailliet 1988). However, it is noted that the Bat Ray is a considerably larger species (reaching 180 cm DW) than the Banded Eagle Ray.
Taxon
Taxa
Aetomylaeus nichofii | (Bloch & Schneider, 1801)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
Aetomylaeus caerulofasciatus has recently been described as distinct from the wider-ranging Indo-West Pacific A. nichofii (White et al. 2015).
Taxon distribution as listed in assessment
The Banded Eagle Ray occurs throughout UAE waters (Randall 1995, Carpenter 1997, Hellyer and Aspinall 2005, Environment Agency Abu Dhabi unpublished data). Globally, it is widespread in the Indo-West Pacific (Spaet and Berumen 2015, Last et al. 2016).
Assessed status
Asessment status in full
Vulnerable
Assessment status abreviation
VU
Assessment status criteria
A2cd
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 Banded Eagle Ray occurs throughout UAE inshore waters, and is common. This species is not targeted or valued in markets of the UAE and trawling has been banned there since 1980. It is caught as bycatch in inshore gill net fisheries. It is under extremely intense and increasing demersal fishing pressure in much of the Arabian Sea region, and declines have been detected in Pakistan, India and the Red Sea. The loss and degradation of coastal habitats in the Gulf is a significant concern. It is especially susceptible to exploitation (target and bycatch) in many largely unregulated gill net, longline and trawl fisheries that operate within its range outside and surrounding UAE waters. Some management measures are now in place in the Arabian Sea region, although domestic fisheries are likely to continue. Though data specifically from the UAE are not available, individuals in the UAE are a component of a larger, interconnected and migratory population that occurs broadly in the north-western Indian Ocean. It is inferred that declines reported in the Arabian Sea region are representative of its status in the UAE. Based on recorded levels of exploitation and decline in habitat quality, it is suspected to have declined by at least 30% over the past three generation lengths, or about 45 years. It is listed as Vulnerable A2cd.
Criteria system
Criteria system specifics
IUCN v3.1
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
This species is impacted by fisheries in the UAE and forms a relatively large portion of all landed batoids. It is impacted by bycatch fisheries that are active elsewhere in its range as well. Marine habitats in the Gulf are experiencing high levels of disturbance and quickly deteriorating due to major impacts from development activities (including dredging and reclamation), desalination plants, industrial activities, habitat destruction through the removal of shallow productive areas and major shipping lanes (Sheppard et al. 2010).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Aetobatus ocellatus | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
Yes
Habitat
Habitat details as listed in assessment
The Spotted Eagle Ray is found in tropical and warm-temperate waters in coastal regions and over the continental shelf from the surface up to 40 m depth (Weigmann 2016). It sometimes enters lagoons and estuaries and is often associated with coral reef ecosystems (Homma et al. 1994, Last and Stevens 2009). It is also encountered well offshore in open water (Last et al. 2010). It attains a maximum size of 330 cm disc width (DW), but the species is more commonly observed to about 160 cm DW (Last et al. 2010). This species is reported to reach sexual maturity after 4-6 years (Last and Stevens 2009). Size at maturity is reported as 150-160 cm DW (Schluessel et al. 2010, Last et al. 2016) for females, and between 119-130 cm DW for males (Schluessel et al. 2010, Moore et al. 2012). Size at birth is 33-36 cm DW (Last et al. 2010). Reproduction is viviparous with aplacental histotrophy (Last et al. 2010). Little information is available on reproductive biology, although it is known to have up to 10 pups but usually about four pups per litter (Last et al. 2016). Gestation has been reported at 12 months and reproductive periodicity may not be annual (Schluessel et al. 2010). Generation length was inferred as ~15 years based on data for the Bat Ray (Myliobatis californicus) which are reported to have a maximum age of 24 years and an age at maturity of five years (Martin and Cailliet 1988).
Taxon
Taxa
Aetobatus ocellatus | (Kuhl, 1823)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
Aetobatus ocellatus (Kuhl, 1823) was previously considered to be an Indo-West and Central Pacific form of the wider ranging Aetobatus narinari (Euphrasen, 1790). Comparative analysis of the morphology, molecular and parasite diversity has resulted in the redescription of A. ocellatus from tropical and warm-temperate waters of the Indian Ocean and West-Central Pacific Ocean with A. narinari being restricted to the Atlantic Ocean (Richards et al. 2009, White et al. 2010). Molecular analyses suggest greater levels of speciation within the Aetobatus genus, with distinguishable groups in the Western Indian Ocean and Northwest Pacific (Schluessel et al. 2010, White et al. 2010). Samples from Qatar cluster separately -- designated as A. cf. ocellatus 2 (D. Ebert pers. comm. 2017). This requires further examination to delineate species boundaries.
Taxon distribution as listed in assessment
The Spotted Eagle Ray occurs throughout UAE waters. Globally, it is widespread in the Indo-West-Central Pacific (Last et al. 2016).
Assessed status
Asessment status in full
Vulnerable
Assessment status abreviation
VU
Assessment status criteria
A2cd
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This inshore and offshore eagle ray occurs throughout UAE waters. The species inhabits lagoons and estuaries and is often associated with coral reefs. It may be taken as bycatch in certain fisheries. Most of the distribution of the species in the Arabian Sea region is under extremely intense and increasing demersal fishing pressure, especially off Iran, India and Pakistan; although, pressure is thought to be lower in the western part of the Arabian Sea, which includes the UAE. Furthermore, the loss and modification of coastal habitats across the region is a significant concern. Its relative rarity, large size and low productivity makes this species particularly susceptible to population decline as a result of fishing pressure and coastal development. Though data specifically from the UAE are not available, individuals in the UAE are a component of a larger, interconnected and migratory population that occurs broadly in the north-western Indian Ocean. Given the intense fishing pressures faced by this species throughout the Arabian Seas, and ongoing threats from bycatch and habitat loss, it is inferred that declines reported in the Arabian Seas are representative of the status in the UAE. Based on recorded levels of exploitation and declines in habitat quality, it is suspected to have declined by 30-50% over the past three generation lengths, or about 45 years. It is listed as Vulnerable A2cd.
Criteria system
Criteria system specifics
IUCN v3.1
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
The Spotted Eagle Ray is highly susceptible to a variety of inshore demersal fisheries, including trawls and gill nets. Its small litter size, schooling behaviour, inshore habitat and hence availability to a wide variety of inshore fishing gear (beach seine, gillnet, purse seine, benthic longline, trawl, etc.), and the generally intense and unregulated nature of inshore fisheries across large parts of the species' range, pose significant risks to the Arabian Sea population. The occurrence of this species in coral reef areas make it susceptible to habitat degradation and coastal development, pollution, and the effects of climate change (Normile 2016). In the Arabian Gulf, there are major impacts from from development activities (including dredging and reclamation), desalination plants, industrial activities, habitat destruction through the removal of shallow productive areas and major shipping lanes (Sheppard et al. 2010). Corals in the UAE and Arabian Gulf have severely declined due to the increasing frequency of mass bleaching events caused by rising water temperatures, which is a consequence of climate change, as well as pervasive coastal development (Riegl et al. 2018, Burt et al. 2019).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Curruca curruca | UAE National Red List of Birds

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 inhabits a variety of lightly wooded, bushy country, including woodland, dense undergrowth, acacia scrubland, thick bushes, parks, large gardens, oases and cultivations (Richardson 1990, Aspinall and Porter 2011). There is no information available about its diet in the UAE; elsewhere the diet is made up of mostly insects in the breeding season and fruits at other times of the year, although it is generally considered less frugivorous than many congeners. The species is a long-distance migrant, breeding between late April and early August throughout Eurasia (Aymí and Gargallo 2015).
Taxon
Taxa
Curruca curruca | (Linnaeus, 1758)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxonomic Notes
Previously placed in Sylvia (del Hoyo and Collar 2016) but moved to current genus following Cai et al. (2019). Until recently considered to constitute several species, with splits of althaea and minula (with margelanica) (Sibley and Monroe 1990, 1993) from curruca (AOU 1998 and supplements; Dowsett and Forbes-Watson 1993; Sibley and Monroe 1990, 1993), and this may ultimately be more appropriate. Nuclear DNA, however, fails to support clades based on mtDNA, and, although althaea is relatively well marked, characters used to define species (and subspecies) limits prove too weak for taxa to pass tests of diagnosability (Olsson et al. 2013b). Treatment of these forms under a single species currently therefore inevitable (Dickinson and Christidis 2014).Geographical variation largely clinal, subspecies halimodendri intergrading widely with nominate in S Siberia. Proposed subspecies caucasica (Turkey, Caucasus and N Iran) and zagrossiensis (SW Iran) barely separable from nominate; similarly, telengitica (Russian Altai and Mongolia) included in margelanica. Proposed subspecies snigirewskii (Turkmenistan) largely inseparable from minula, and jaxartica (S Kazakhstan) falls within range of clinal variation of halimodendri; poorly differentiated chuancheica (upper R Huang He, S of Gobi, in N China) included in margelanica. Birds from Alai and Pamir Ranges E to Tien Shan sometimes separated as subspecies monticola, but not reliably distinguishable from those in rest of range of althaea. Six subspecies recognized.
Taxon distribution as listed in assessment
Two/three subspecies occur during passage and winter in wooded areas throughout the UAE. Subspecies curruca/blythi is fairly common on passage between mid-February and mid-May and between September and November. In winter, it is uncommon (Pedersen et al. 2017). Subspecies halimodendri is common on passage and winter, occurring in the UAE between mid-September and mid-April (Pedersen et al. 2017). Individuals wintering in or passing through the UAE breed throughout Eurasia.
Assessed status
Asessment status in full
Vulnerable
Assessment status abreviation
VU
Assessment status criteria
D1
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 small non-breeding population size of this species in the UAE means that the species triggers the threshold for Vulnerable under Criterion D.
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 intensification of modern agricultural techniques has driven habitat loss and declines in this species in some areas within its global range (Hagemeijer and Blair 1997), but it is unknown whether individuals that visit UAE are impacted by this threat. Overgrazing outside of Protected Areas may have an impact on this species.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
It is assessed that in 1996, the national Red List status of this species would have been the same as in this assessment.
Verified entry
Off

Anthus cervinus | UAE National Red List of Birds

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 occurs in humid areas and usually near water, favouring marshes, damp grassland, wet hollows, surface water margins and cultivations (Richardson 1990, Aspinall and Porter 2011). During winter, the species forms small flocks at its preferred locations (Richardson 1990). There is no information available about its feeding habits in the UAE; elsewhere it forages on the ground and its prey is mainly insects but also other invertebrates, and some vegetable matter (Tyler 2016). The species is migratory and breeds between late May and July in the arctic tundra.
Taxon
Taxa
Anthus cervinus | (Pallas, 1811)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species occurs in the UAE during winter and on passage. Numbers are highest between mid-September and early May, when the species is common to very common in humid areas throughout the country (Pedersen et al. 2017). Individuals wintering in or migrating through the UAE breed in the Arctic.
Assessed status
Asessment status in full
Vulnerable
Assessment status abreviation
VU
Assessment status criteria
D1
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 very small non-breeding population size within the UAE, small enough that it falls below the threshold for listing as Endangered under Criterion D. However, it is likely that there is the chance for a rescue effect for this population and so the category has undergone a regional adjustment. Therefore, the species is listed here as Vulnerable under Criterion D1.
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
Artificial habitats that favour this species may be transient, so monitoring of such habitats will be important. The species is also vulnerable to future climate change (Virkkala et al. 2008).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
It is assessed that in 1996, the national Red List status of this species would have been the same as in this assessment.
Verified entry
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Motacilla cinerea | UAE National Red List of Birds

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 occurs on inland freshwater sites, including wooded streams, mountain wadis near rivers, pools and pool margins, sewage treatment plants and wet grassland (Richardson 1990, Aspinall and Porter 2011). There is no information available about its diet in the UAE; elsewhere it feeds mainly on insects, but also takes freshwater shrimps (Gammarus), terrestrial snails and spiders. The species is migratory and breeds between late March and August near watercourses in Eurasia.
Taxon
Taxa
Motacilla cinerea | Tunstall, 1771
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxon distribution as listed in assessment
The majority of occurrences of this species within the UAE are likely to be of wintering birds and migrant individuals on passage to and from the breeding grounds (Pedersen et al. 2017). Numbers are highest between late August and April, when the species is fairly common at freshwater sites throughout the country. The species is rarely observed in May (Pedersen et al. 2017). Individuals wintering in or passing through the UAE breed throughout Eurasia.
Assessed status
Asessment status in full
Vulnerable
Assessment status abreviation
VU
Assessment status criteria
D1
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
Retained in the UAE list because of its regional status as a breeding bird in the Arabian Peninsula, within the UAE this species has an extremely small non-breeding population size. This tiny population size meets the threshold for listing as Critically Endangered under Criterion D. However, after regional adjustment it is listed here as Vulnerable under Criterion D, as it has a relatively small population size in UAE compared to the regional and global population.
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
Symes et al. (2015) do not note any specific threats for this species despite it being considered Near Threatened as a breeding bird in the Arabian Peninsula due to a small population size; and indeed it has been suggested that stream pollution may not significantly impact the species (del Hoyo et al. 2004). Artificial habitats that favour this species may be transient, so monitoring of such habitats will be important.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
It is assessed that in 1996, the national Red List status of this species would have been the same as in this assessment.
Verified entry
Off

Motacilla citreola | UAE National Red List of Birds

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 occurs near waterbodies or wet areas, including swampy and damp meadows or fields, marshes, exposed pond edges, river and lake margins, public parks, golf courses, lagoons, sewage ponds and water treatment plants (Richardson 1990, Aspinall and Porter 2011). There is no information available about its diet in the UAE; elsewhere the diet includes a wide variety of invertebrates, often aquatic, and their larvae. The species is migratory and breeds from April to June in central Eurasian grasslands.
Taxon
Taxa
Motacilla citreola | Pallas, 1776
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxon distribution as listed in assessment
The majority of occurrences of this species within the UAE are likely to be of wintering birds and migrant individuals on passage to and from the breeding grounds. Numbers are highest between mid-August and April, when the species is common at wetlands throughout the country (Aspinall and Porter 2011, Pedersen et al. 2017). In other months, the species is rare (Pedersen et al. 2017). Individuals wintering in, or migrating through, the UAE breed throughout central Eurasia.
Assessed status
Asessment status in full
Vulnerable
Assessment status abreviation
VU
Assessment status criteria
D1
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 non-breeding population size that is small enough to qualify as Endangered under Criterion D. However, the species is considered likely to receive a rescue effect from breeding populations outside of the country and so the species's category has undergone a regional adjustment. It is therefore listed as Vulnerable under Criterion D1.
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 are currently no known significant threats to this species, however, artificial habitats that favour this species may be transient, so monitoring of such habitats will be important.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
It is assessed that in 1996, the national Red List status of this species would have been the same as in this assessment.
Verified entry
Off

Acrocephalus scirpaceus | UAE National Red List of Birds

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 breeds in thick beds of reed (Phragmites particularly P. australis) on damp soil near water (Jennings 2010, Aspinall and Porter 2011). It also prefers this habitat during migration, but additionally uses any thick vegetation, bushes or undergrowth (Jennings 2010). There is no information available on its diet in the UAE, but elsewhere it mainly feeds on insects and spiders, which are taken from reeds or nearby vegetation, and occasionally on vegetable matter (Jennings 2010). The breeding period lasts from February to July or even longer, suggesting that the species is double-brooded (Jennings 2010). No nest has been described in the UAE, but elsewhere it is a deep cup neatly woven from split reed blades, reed inflorescences, plant down and grass stems and lined with finer material. It is suspended from two to eight vertical reed stems, usually 15-“200 cm over shallow water. Outside Arabia, clutches can be three to five eggs, but are most commonly four.
Taxon
Taxa
Acrocephalus scirpaceus | (Hermann, 1804)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxon distribution as listed in assessment
The majority of occurrences of this species within the UAE are of migrant individuals on passage to and from the breeding grounds, with highest numbers between February and May and between July and November (Pedersen et al. 2017). Since 1992, the species is regularly breeding in the UAE, and it has been suggested that a part of this population could be resident within the country (Jennings 2010, Pedersen et al. 2017).
Assessed status
Asessment status in full
Vulnerable
Assessment status abreviation
VU
Assessment status criteria
D1
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 relatively small breeding population for this species meets the threshold for listing as Endangered under criterion D. However, the population is thought to be continuing to increase, and there is likely a rescue effect for this species. Therefore, after regional adjustment, the species is listed here as Vulnerable under criterion D1.
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
Loss of wetland sites due to development is likely to be the main threat to this species (see Aspinall 1996), and potential turnover in certain artificial wetland habitats could impact the species's habitat.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
This species has increased its population size since 1996 due to increasing availability of suitable irrigated 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 Endangered under criterion D then, whereas now (2019) it is assessed as Vulnerable.
Verified entry
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