United Arab Emirates

Official name
United Arab Emirates
ISO alpha-2 code
AE
ISO alpha-3 code
ARE
ISO numeric-3 code
784
Continent
Asia

Galerida cristata | 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 grassy or arid country and semi-desert, given that sufficient vegetation cover is present (Jennings 2010). It is particularly numerous near human settlements, on farmlands, gardens and cultivated areas, as well as along roadsides (Jennings 2010, Aspinall and Porter 2011). The species generally becomes scarcer with increasing aridity and distance from human habitations (Jennings 2010). It feeds on the ground, occasionally digging into the surface with the bill (Jennings 2010). It feeds on invertebrates and plant material, such as seeds. Elsewhere, it also feeds on human food scraps, such as bread, fruits and plant shoots (Jennings 2010). The availability of drinking water is important for this species (Jennings 2010). The breeding behaviour is not well explored. In Arabia, the breeding period peaks between May and June, but nesting may already occur from January on (Jennings 2010). The species is monogamous and usually lays a clutch of one to five eggs. The nest is a depression on the ground with an untidy lining of grass or other vegetation (de Juana and Suárez 2004), which placed in the shade of a clump of grass or other plants (Jennings 2010).
Taxon
Taxa
Galerida cristata | (Linnaeus, 1758)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species is a very common, abundant resident occurring almost across the entire country (Pedersen et al. 2017). It has colonised Qarnayn, Abu al-Abyad and Das islands in the 1990s, as well as remote desert areas in the south and west of the UAE (Richardon 1990, Jennings 2010, Pedersen et al. 2017).
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species has a very large resident population within the UAE, which is suspected to be potentially increasing. Therefore, it is listed here as Least Concern.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
In Europe the use of pesticides has negatively affected populations (Tucker and Heath 1994), but this may not be a significant threat to this species within UAE. Predation by cats,;Felis catus,;has been noted to cause local declines on the Arabian Peninsula (Symes et al. 2015). Overgrazing outside of Protected Areas could be be an additional threat 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

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.
Verified entry
Off

Ammomanes deserti | 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 arid hills and along sparsely vegetated stony or rocky slopes (Jennings 2010). It avoids flat and sandy landscapes. The species can survive long periods without drinking water and shows several behavioural and morphological adaptations to hot and arid conditions: It is most active around sunrise and sunset, it moves slowly, avoids long flights and pants in hot weather. Moreover, its plumage has wide bar gaps between feathers (Jennings 2010). The species feeds on seeds and invertebrates, which it takes by systematically searching rocks and vegetation. Occasionally, it visits human habitations where it picks up discarded food (Jennings 2010). The highest breeding activity in Arabia has been recorded in March (Jennings 2010). The nest is made from grass stems and other fine plant material, lined with softer material and with a rampart of small stones on the exposed side, or surrounded by small stones when in an open site. It is always placed on the ground in the shade of a rock or plant (Jennings 2010). Clutches mostly contain three eggs (Jennings 2010).
Taxon
Taxa
Ammomanes deserti | (Lichtenstein, 1823)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species is a common resident, occurring in the mountains and plains of northeastern UAE as well as locally along the coast of western Abu Dhabi Emirate (Pedersen et al. 2017).
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species has a relatively large resident population in the UAE. The breeding population in the wider Arabian Peninsula is stable; thus, the potential for immigration from outside the UAE remains very high. Therefore, the species is listed as Least Concern 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
Development within its range could be leading to the loss and degradation of its habitat.
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

Ammomanes cinctura | 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 found in arid open desert plains with scattered vegetation and gravelly, sandy or stony rises (Aspinall and Porter 2011). It avoids proximity to humans (Jennings 2010). There is no information available on its diet in Arabia, but it is assumed that the species mainly feeds on seeds, which it collects in small groups on the ground (Jennings 2010). For thermoregulation, it retreats to shady areas beside rocks or trackside debris like discarded tyres, and regularly visits the holes of Spiny-tailed Lizard Uromastyx microlepis during the hottest times of the day (Jennings 2010). The breeding period likely lasts from March to June (Jennings 2010). The nest consists of a cup made from twigs and grasses, lined with finer grasses, plant downs and feathers, which is dug into the ground. It is protected by a small wall made from pebbles. Nests are placed on the northern or north-eastern side of rocks or plants in order to grant shade to the incubating birds, eggs and nestlings (Jennings 2010).
Taxon
Taxa
Ammomanes cinctura | (Gould, 1839)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species is uncommon in the UAE. It is highly localised mainly along the coast of Abu Dhabi and Dubai emirates (Pedersen et al. 2017).
Assessed status
Asessment status in full
Critically Endangered
Assessment status abreviation
CR
Assessment status criteria
D
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species has an extremely small breeding population in the UAE, which qualifies it for listing as Critically Endangered. It is uncertain whether it would receive any rescue effect from outside of the country, and so it is retain here under this category.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
As for Greater Hoopoe-Lark Alaemon alaudipes, the most severe threat to this species comes from land-use changes to its desert habitat (Aspinall 1996). Overgrazing outside of Protected Areas could also be an issue.
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

Eremopterix nigriceps | 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 a wide range of habitats, preferring semi-desert and sandy or stony plains with low scrub and grass vegetation (Jennings 2010, Aspinall and Porter 2011). It is also frequently found along the edge of cultivations, along roadsides, on salt flats and on coastal dunes (Jennings 2010, Aspinall and Porter 2011). It feeds on the ground or in small bushes, taking mainly seeds, insects and caterpillars (Jennings 2010). During the hottest time of the day, it retreats to shaded areas where it often prostrates on the ground or in holes of Spiny-tailed Lizard Uromastyx microlepis (Jennings 2010). The breeding period is usually in spring, but breeding may occur year-round, depending on environmental conditions like temperature, humidity and rainfall (Jennings 2010). The nest is a small cup dug in the ground, which is lined with grass or soft stems and leaves. It is placed at the base of vegetation, preferably Anabasis articulata, and positioned to avoid the afternoon sun (Jennings 2010). Clutches contain two to four eggs (Jennings 2010). Outside of the breeding season, the species is nomadic, forming large flocks to move inland away from the breeding grounds (Jennings 2010, Pedersen et al. 2017).
Taxon
Taxa
Eremopterix nigriceps | (Gould, 1839)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species is a common resident occurring throughout the UAE (Pedersen et al. 2017).
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species has a relatively large resident population in the UAE. The breeding population in the wider Arabian Peninsula is stable; thus, the potential for immigration from outside the UAE remains very high. Therefore, the species is listed as Least Concern 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
There are no significant threats to this species within the UAE (Aspinall 1996), although overgrazing outside of Protected Areas could potentially be an issue.
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

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.
Verified entry
Off

Argya squamiceps | 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 prefers dry acacia and other scrub habitat, particularly wooded savanna, but also occurs in plantations, urban areas, gardens, shelter belts and around farmland, given that sufficient bushy cover is provided (Jennings 2010, Aspinall and Porter 2011, S. Alam in litt. 2019). It generally avoids open desert and rocky areas, forests and urban areas (Jennings 2010). It forages in groups mainly on the ground, searching under stones or scratching and digging with the bill, but also gleans bushes and trees (Jennings 2010). Its diet consists of ground-dwelling invertebrates and vegetable matter or dates (Jennings 2010). The species is group-living. The breeding season typically lasts from March to July, but may be advanced when food availability is high (Jennings 2010). Nests are bulky cups made of grass and twigs, lined with hair, grass and rootlets, and placed in acacia or other trees and bushes. Clutch size is unknown for the UAE, but elsewhere in Arabia they consist of one to six eggs (Jennings 2010).
Taxon
Taxa
Argya squamiceps | (Cretzschmar, 1827)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxonomic Notes
Argya squamiceps (del Hoyo and Collar 2016) was previously listed as Turdoides squamiceps.
Taxon distribution as listed in assessment
This species is a common resident in the UAE, occurring in the northern and eastern part of the country (Pedersen et al. 2017). In the 1990s, the range expanded westward close to Abu Dhabi City (Jennings 2010).
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species has a relatively large resident population within the UAE, and there is no evidence for a population decline. Therefore, the species is assessed here as Least Concern.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
This species suffers from habitat loss and deterioration in UAE (Aspinall 1996). This is as a result of tree felling, with grazing pressure reducing regeneration (Aspinall 1996). Local water abstraction also likely has an impact (Aspinall 1996).
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 stentoreus | 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
Along the coast, this species occurs in stands of mangrove, mainly Grey Mangrove Avicennia marina, favouring low, thick stands over tall, open trees (Jennings 2010). Further inland and at freshwater sites near the coast, the species is found in Phragmites reed beds (Jennings 2010). During winter, the species ranges into a wider variety of habitats, including scrub, woodland and date gardens (Aspinall and Porter 2011). The species is secretive, reluctant to fly and generally keeps under vegetation cover (Jennings 2010). It feeds mainly on insects and was once observed killing a gecko (Jennings 2010). In mangrove habitat, it forages on exposed mud near the base of trees and gleans foliage; in reed beds it picks prey from or near the water surface (Jennings 2010). The breeding period lasts from March to early July, when up to three eggs are laid. Nests can be constructed from grass and twigs and woven to branches (Jennings 2010). It has been suggested that the species is double-brooded, but this has not been conclusively proven yet (Jennings 2010).
Taxon
Taxa
Acrocephalus stentoreus | (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 in the UAE. It is most common along the coast, but occurs locally at wetlands further inland (Pedersen et al. 2017).
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
The relatively small breeding population for this species potentially could warrant a listing as Near Threatened under criterion D1. 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 Least Concern.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
No major threats are known for this species, but urban expansion could have an impact in the future; and 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
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 Near Threatened under criterion D1 then, whereas now (2019) it is assessed as Least Concern.
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.
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Prinia gracilis | 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 densely vegetated, damp areas, such as irrigation ditches, reed beds, sewage farms, cultivated areas and date groves, farmland, but also gardens and parks (Jennings 2010). It generally avoids dry environments (Jennings 2010). It forages by hopping through the vegetation and picking items from leaves, taking a variety of insects (Jennings 2010). The species is generally sedentary and very reluctant to fly (Jennings 2010). Males are territorial throughout the year (Jennings 2010). The breeding period lasts from February to June, and clutches contain three to four eggs (Jennings 2010). The male constructs the nest and the female assists by lining the cup. It is an oval structure made of dry grass and other plant material, spider cocoons and spider web and hidden low above the ground in dense vegetation, like fairly tall grass or bushes. Nest construction may exceptionally take up to seven weeks in the UAE (Jennings 2010).
Taxon
Taxa
Prinia gracilis | (Lichtenstein, 1823)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species is a very common resident in the UAE (Pedersen et al. 2017).
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species has a relatively large resident population size within the UAE, which is increasing. Therefore, it is considered to be Least Concern within the country.
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
Within the UAE there are not thought to be any significant threats (Aspinall 1996), although overgrazing outside of Protected Areas potentially could 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
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