NT

Nannorrhops ritchieana | 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
This plant species is described as perennial tree with fan-shaped leaves forming clumps several meters across that generally occurs in gravelled areas along low wadi banks (Jongbloed et al. 2003). According to G.R. Feulner (in lit, MEW 2010), the species is normally found at places where wadi broaden and silt accumulates.
Taxon
Taxa
Nannorrhops ritchieana | (Griff.) Aitch.
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 along the western slopes of the Hajar Mountains from Shawka, south to the border with Oman (Jongbloed et al. 2003, Feulner 2011). The species also occurs on Jebel Hafeet (Perry 2008) on the northern summit wadi on Jebel Hafeet (at almost 1,000 m asl; G.R. Feulner, in lit. MEW 2010), where it persists (S. Sakkir and G. Brown pers. comm. 2018). According to G.R. Feulner (in lit. MEW 2010), this species ""is consistently present as one or a few clumps/groves in almost every wadi from Shawka south [to the Oman border], normally at places where the wadi broadens for one reason or another and silt accumulates. It is relatively common in the wadis in the greater Juwaif area, about half-way between the Hatta Road and Mahdhah."" The Sharjah Seedbank & Herbarium (SSBH) recorded the species from the Al Dhaid-Masafi road (Thaoban), and found four new clumps of the plant in Al-Bardy and Al-Wishah (in gravelly area east of Dhaid); these clumps are located inside farms, and local people reported that ""...they planted it"" a long time ago (T. Mahmoud pers. comm. 2019). The EOO is estimated at between 1,500 and 2,000 km<sup>2</sup>, whilst the AOO is less than 500 km<sup>2 </sup>and is likely to be as little as 300 km<sup>2</sup>. The species also occurs in adjacent areas of Oman (G.R. Feulner in lit. MEW 2010). Globally, the species is native from the southern Arabian Peninsula to Iran and Pakistan (Board of Trustees, RGB Kew 2018).
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
Assessment status criteria
B1a+2a
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 occurs in the Hajar Mountains from Masafi (Wadi Ham south to the border with Oman, including Wadi Hatta), and also occurs on Jebel Hafeet. some subpopulations may be the result of intentional cultivation for use. The extent of occurrence (EOO) is between 1,500 and 2,000 km<sup>2</sup>, and the AOO at less than 500 km<sup>2</sup>. There is no information on population size or trend. The species is assessed as Near Threatened as, whilst the extent of occurrence (EOO) and area of occupancy (AOO) are restricted, and it is suspected that the species occurs in between eight and ten locations, there is no evidence of widespread threats within its distribution range, or of continuing decline. The species would qualify as Vulnerable if a continuing decline in the number of mature individuals, or in habitat area, extent or quality was known or suspected. In addition, the species might potentially qualify as threatened under criterion D, however further information on the population structure of this probably clonal species is required.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
MEW (2010) considered populations fragmented and at threat from development, without giving details. At one site in the Hajar Mountains, quarrying activities had lowered the wadi floor by at least 2 m, with consequential impacts on the ground water level. As a result, one cluster of the palm in the wadi is dying (D. Aplin pers. comm. 2019). The species is generally found in the lower parts of wadis and it is therefore vulnerable to development, e.g. road construction, and other works.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
The situation for this species in 1996 is thought to be similar to the situation for the species now.
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Brevitrygon walga | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
Yes
Habitat
Habitat details as listed in assessment
This species is very common in shallow and intertidal waters over soft substrates mostly to 30 m, but occasionally 40 m (K.V. Akhilesh pers. comm. 05/02/2017). It is a very small species, only growing to 32 cm disc width (DW). Data from the H. imbricata form show that males mature about 18 cm DW and females by at least 23 cm DW (Moore et al. 2012). It is born at 7-10 cm DW (Last et al. 2016). No data on litter size is available, but given the small size, it is likely to be low. Similarly, no data on frequency of breeding or on ageing are available. Generation length is estimated from the similar-sized Speckled Maskray (Neotrygon picta) from Australia that matures at 3-4 years and reaches a maximum age of 18 years, yielding a generation length of ~11 years (Jacobsen and Bennett 2010).
Taxon
Taxa
Brevitrygon walga | (Müller & Henle, 1841)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
Last et al. (2016a) placed Himantura heterurus, H. imbricata, H. javaensis, and H. walga within the new genus Brevitrygon, previously confused with other dwarf whiprays (Brevitrygon species) (Last et al. 2016b). There remains considerable taxonomic confusion over 'B. walga' with different forms across its range. These may turn out to represent a series of different species.
Taxon distribution as listed in assessment
The Scaly Whipray occurs throughout UAE waters. It is restricted to the Arabian Sea region, although its true distribution is unclear due to significant taxonomic issues, and research is urgently required to resolve this. Forms apparently consistent with the illustration in Last et al. (2016) appear to be present in eastern Iran waters of the Sea of Oman (F. Owfi unpub. data). However, specimens from the northern Arabian Gulf (hereafter referred to as the 'Gulf') (Kuwait and Iran; previously reported as Himantura imbricata) appear notably different (A.B.M. Moore unpub. data) and more consistent with the Bengal Whipray (Brevitrygon imbricata), a species that Last et al. (2016) report only from the Bay of Bengal region. Additional variation is evident in India. Until taxonomy is resolved, the forms are treated as a single species for the purposes of this assessment.
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
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 Scaly Whipray occurs throughout UAE shallow waters, and can be common. Within the Arabian Sea region, it is regularly caught in shallow water trawls and is normally discarded at sea in the western part, but landed in considerable numbers in the eastern part (i.e., India). This species is not targeted or valued in markets of the UAE, trawling has been banned there since 1980, and recently conducted surveys indicate it remains common in the area. It is, however, discarded in large numbers and it is unknown how impactful this threat is to the species. 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 20-30% over the past three generation lengths, or about 33 years. It is listed as Near Threatened, nearly meeting the thresholds for 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
Information pertaining to threats specific to the UAE are unavailable. This species is impacted by bycatch fisheries that are active elsewhere in its range. 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:

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Pastinachus sephen | 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 Cowtail Ray is benthic in coastal habitats and occurs over soft substrates, often near coral reefs (Last et al. 2016) to depths of 60 m. Maximum size and biology is poorly known due to confusion amongst Pastinachus spp. This species reaches at least 89 cm disc width (Last et al. 2016). Generation length is estimated at 20 years based on age data from Maculabatis astra (Jacobsen 2007).
Taxon
Taxa
Pastinachus sephen | (Forsskål, 1775)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
The Cowtail Ray occurs throughout UAE waters. It is possibly endemic to the Arabian Sea region, although its exact distribution is uncertain due to confusion amongst Pastinachus species, and recent taxonomic changes within the genus (Last et al. 2016).
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
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 Cowtail Ray occurs throughout UAE coastal waters. The exact distribution is uncertain due to confusion amongst Pastinachus species and recent taxonomic changes. This species is not targeted or valued in markets of the UAE, trawling has been banned there since 1980 and recent surveys have detected it in the area. Cowtail rays are regularly discarded in the Arabian Gulf and Sea of Oman. A large part of the species' regional distribution (namely, India and Pakistan) is under extremely intense and increasing demersal fishing pressure. It is not known how individuals occupying the UAE are connected with the broader population of the Arabian Seas region, and there is no information available to suggest that its population status differs in the UAE as compared to other parts of its range in the region. Given the threats faced by this species in other parts of the Arabian Seas region, and ongoing threats from discarding and habitat loss in the UAE, 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 decline in habitat quality, it is suspected to have declined by 20-30% over the past three generation lengths, or about 60 years. It is listed as Near Threatened, nearly meeting the thresholds for 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
No
Endemism Notes
Is an endemic?: No
Endemism specifics: Possibly endemic to Arabian Sea region
Conservation
Threats listed in assessment
Information pertaining to threats specific to the UAE are unavailable. This species is impacted by bycatch fisheries that are active elsewhere in its range. 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). Corals in the UAE and Arabian Gulf have severely declined due to the increasing frequency of mass bleaching events caused by rising water temperatures, which is a consequence of climate change, as well as pervasive coastal development (Riegl et al. 2018, Burt et al. 2019).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
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Pastinachus ater | 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 Broad Cowtail Ray is benthic in coastal habitats. Maximum size and biology is poorly known due to confusion amongst other cowtail rays. Reaches ~200 cm disc width (Last et al. 2016). Generation length is estimated at 20 years based on age data from Maculabatis astra (Jacobsen 2007).
Taxon
Taxa
Pastinachus ater | (Macleay, 1883)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
Recently, molecular data confirmed that the single, widespread Indo-“Pacific species, Pastinachus sephen consists of two species, the widespread P. ater and a more restricted P. sephen (Last et al. 2016a).
Taxon distribution as listed in assessment
The Broad Cowtail Ray occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific, although its exact distribution is uncertain due to confusion amongst Pastinachus species and recent taxonomic changes within the genus.
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
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 Broad Cowtail Ray occurs throughout UAE coastal waters. The exact distribution is uncertain due to confusion amongst Pastinachus species and recent taxonomic changes. This species is not targeted or valued in markets of the UAE, trawling has been banned there since 1980 and recent surveys have detected it in the area. Cowtail rays are regularly discarded in the Arabian Gulf and Sea of Oman. A large part of the species' regional distribution (namely, India and Pakistan) is under extremely intense and increasing demersal fishing pressure. It is not known how individuals occupying the UAE are connected with the broader population of the Arabian Seas region, and there is no information available to suggest that its population status differs in the UAE as compared to other parts of its range in the region. Given the threats faced by this species in other parts of the Arabian Seas region, and ongoing threats from discarding and habitat loss in the UAE, 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 decline in habitat quality, it is suspected to have declined by 20-30% over the past three generation lengths, or about 60 years. It is listed as Near Threatened, nearly meeting the thresholds for 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
Information pertaining to threats specific to the UAE are unavailable. This species is impacted by bycatch fisheries that are active elsewhere in its range. 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
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Butorides striata | 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 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).
Taxon
Taxa
Butorides striata | (Linnaeus, 1758)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxonomic Notes
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).
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).
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
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 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.
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 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).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
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.
Verified entry
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Alaemon alaudipes | 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 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)
Taxon
Taxa
Alaemon alaudipes | (Desfontaines, 1789)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
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).
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
Assessment status criteria
C2a(ii)
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 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).
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
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.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
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.
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Curruca mystacea | 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 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).
Taxon
Taxa
Curruca mystacea | (Ménétries, 1832)
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). 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.
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.
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
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 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.
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 not thought to be any current significant threats to this species, however, 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
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.
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Pycnonotus xanthopygos | 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
The main habitat of this species are wadis and acacia scrub (Jennings 2010). It is also frequently found in well-vegetated parks, gardens and palm groves (Aspinall and Porter 2011). It feeds mostly on fruit, as well as on seeds and invertebrates and less frequently on nectar, leaves and flowers (Fishpool and Tobias 2005, Jennings 2010). Occasionally, it takes human food scraps and visits bird tables (Jennings 2010). Pairs establish a permanent bond. The breeding season can last from January to September, but peaks between March and April. There are hints that the species is double-brooded, but confirmation is still lacking (Jennings 2010). Clutches usually consist of less than three eggs, although occasionally four or five have been observed (Jennings 2010). The nest is a cup or small basket of thin twigs, grass stems, moss and leaves with the base constructed of broad leaves (sometimes with newspaper, strips of plastic or cotton wool) and the structure is held together by cobwebs and cotton threads, lined after a fashion with hair, shredded bark and rootlets, apparently sometimes unlined (Fishpool and Tobias 2005, Jennings 2010). It is placed in a bush or tree at least 2 m above ground (Jennings 2010).
Taxon
Taxa
Pycnonotus xanthopygos | (Ehrenberg, 1833)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species is a common resident of the mountains in the northern and eastern part of the UAE (Pedersen et al. 2017). Isolated populations in Abu Dhabi and Dubai, which became established in the 1980s, are thought to potentially originate from escaped or released cage birds, but the species is also native to the UAE;(Jennings 2010, Pedersen et al. 2017). While there is concern that this species might hybridize with other bulbul species in the UAE, evidence for this is lacking (Jennings 2010).
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
Assessment status criteria
C2a(ii)
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
The species is suspected to have declined in the UAE since 1996, and the overall population size within the country is now thought to number &lt;10,000 mature individuals. This qualifies it for listing as Near Threatened under criterion C2a(ii).
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 of montane areas is thought to be a key threat to the species. Introduced bulbuls might have some local impacts on the species as a competitor (Aspinall 1996) [note Aspinall (1996) refers to White-cheeked Bulbul, Pycnonotus leucogenys,;but it is assumed here that this refers to White-eared Bulbul, P. leucotis, per Pedersen et al. (2017)]. Overgrazing outside of Protected Areas could be an additional threat.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
The major threat (and likely primary driver of any population decline in this species ) - development in wadis - has commenced since 1996, so the suspected population decline is likely to have started since 1996. Therefore, it is assessed that in a 1996 assessment the species would have been deemed to be Least Concern.
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Cercotrichas galactotes | 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
The species occurs in parks and gardens, cultivations and date groves, as well as semi-desert and scrubland with good vegetation cover (Jennings 2010, Aspinall and Porter 2011). During migration, the species also occupies very arid places, but it generally avoids dry habitat during the breeding season, when it favours shaded, leafy areas with water readily available (Jennings 2010). It forages on the ground in leaf litter and under dense vegetation, where it takes mostly invertebrates and, especially during migration, also berries of Salvadora persica trees (Jennings 2010). The breeding season lasts from late spring to mid-summer (Jennings 2010). The nest is a loose flat cup of dry grass stems, twigs and bark, lined with fine fibres, hair and feathers. It is built in dense vegetation, often on the trunk of a date palm, on branches, in vines or in tree holes (Jennings 2010). It is possible that the species is double- or even triple-brooded (Jennings 2010).
Taxon
Taxa
Cercotrichas galactotes | (Temminck, 1820)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species occurs throughout the UAE. The country is an important stop-over site for individuals on migration to and from the breeding grounds, and also holds a breeding population of the species between March and September (Pedersen et al. 2017).
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
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 been rapidly increasing within the UAE as a breeding species. The population size is still thought to fall beneath the threshold for listing as Vulnerable, but a regional adjustment of one category has been applied. Therefore, the species is listed here as Near Threatened.
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
Changes to management practices of agricultural land could reduce the available breeding habitat for this species (Aspinall 1996). This involves the removal of overgrown patches at corners and edges of fields as well as the clearance of undergrowth (Aspinall 1996).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
This species is thought to have increased in line with increases in managed areas such as gardens and plantations. After applying a regional adjustment, the species would have been listed as Vulnerable under criterion D1 in 1996, whereas it is listed as Near Threatened now.
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Plegadis falcinellus | 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 wetlands like freshwater and brackish marshes, sewage treatment plants and irrigated grassland (Richardson 1990, Aspinall and Porter 2011). There is no information available about the species's diet in the UAE; elsewhere the diet varies seasonally depending on availability, and the species takes insects, worms, leeches, molluscs, crustaceans and occasionally fish, frogs, tadpoles, lizards, small snakes and nestling birds (del Hoyo et al. 1992, Hancock et al. 1992). It feeds in very shallow water in small flocks of up to 30 individuals (Brown et al. 1982, del Hoyo et al. 1992, Hancock et al. 1992). The species is migratory and breeds in mixed-species colonies throughout southern-central Eurasia (del Hoyo et al. 1992).
Taxon
Taxa
Plegadis falcinellus | (Linnaeus, 1766)
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 August and early May, when the species is locally common at wetlands throughout the country (Richardson 1990, Pedersen et al. 2017). Non-breeding individuals regularly stay in the country over summer (Pedersen et al. 2017).
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
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 in the UAE, which qualifies it for listing as Endangered. However, the species is increasing throughout the Arabian Peninsula; therefore, any breeding population outside of the region will likely have a large rescue effect.; Therefore, the species is retained as Near Threatened at the national level.
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 most relevant threats within UAE are changes in coastal land-use and the possibility of oil pollution, but the severity of these threats towards this species is unknown.Individuals of this species that visit UAE are also threatened by a range of threats that operate outside of the country. For instance the species is threatened by wetland habitat degradation and loss (del Hoyo et al. 1992, Snow and Perrins 1998) through drainage (Marchant and Higgins 1990, Hancock et al. 1992) for irrigation and hydroelectric power production (Balian et al. 2002), clearing, grazing, burning, increased salinity, groundwater extraction and invasion by exotic plants (Marchant and Higgins 1990). It is also threatened locally by hunting (del Hoyo et al. 1992, Snow and Perrins 1998), disturbance and pesticides (del Hoyo et al. 1992), and is susceptible to avian influenza so may be threatened by future outbreaks of the virus (Melville and Shortridge 2006). Climate change may affect the species in the future.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
The population size was very much smaller in 1996, qualifying as CR, however the rate of increase was small, so only decreased by one step through the regional adjustment, to EN. The growth in population is likely linked to increased availability of suitable artificial habitats.
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