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NRLD - 330612 | Curruca curruca

Assessment ID
330612
Taxon name
Curruca curruca
(Linnaeus, 1758)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Curruca curruca
(Linnaeus, 1758)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
sylviidae
Genus
Curruca
Species
curruca
Species authority
(Linnaeus, 1758)
Taxonomic notes and synonyms listed
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.
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Vulnerable
Abbreviated status
VU
Qualifying criteria (if given)
D1
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The small non-breeding population size of this species in the UAE means that the species triggers the threshold for Vulnerable under Criterion D.
Assessment details
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
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.
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
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 (AymĂ­ and Gargallo 2015).
Threats and conservation measures listed
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.
History
It is assessed that in 1996, the national Red List status of this species would have been the same as in this assessment.
Publication
Burfield, I.J., Westrip, J., Sheldon, R.D., Hermes, C., Wheatley, H., Smith, D., Harding, K.A. Allen, D.J. and Alshamsi, O. 2021. UAE National Red List of Birds. Ministry of Climate Change and Environment, Dubai, United Arab Emirates