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NRLD - 330520 | Vanellus vanellus

Assessment ID
330520
Taxon name
Vanellus vanellus
(Linnaeus, 1758)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Vanellus vanellus
(Linnaeus, 1758)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
charadriidae
Genus
Vanellus
Species
vanellus
Species authority
(Linnaeus, 1758)
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
Critically Endangered
Abbreviated status
CR
Qualifying criteria (if given)
D
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This species has a very small non-breeding population in the UAE, which qualifies it for listing as Critically Endangered.;The UAE is situated on the edge of the species range, and occurrence and numbers may be somewhat variable as a result. While the population trend in the UAE is not known, the species is in decline on a global scale. Consequently, breeding populations outside of the country may not have a large rescue effect. Therefore, the species is retained as Critically Endangered at the national level.
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
The majority of occurrences of this species in 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 November and January, when the species is uncommon on open wetlands throughout the country (Aspinall and Porter 2011, Pedersen et al. 2017). The species is rare in February and between September and October (Pedersen et al. 2017). Individuals wintering in or passing through the UAE breed from Europe and northwest Iran through western Russia and Kazakhstan to Siberia, Mongolia and northern China.
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 occurs mainly in wetlands, including marshes, shallow pools, coastal mudflats, creek edges and freshwater margins. It is also found on open fields and grassland, but may tolerate even drier habitats (Richardson 1990, Aspinall and Porter 2011). There is no information available about its diet in the UAE; elsewhere the diet consists mainly of adult and larval insects, spiders, snails, earthworms or frogs (Urban;et al.;1986,;del Hoyo;et al.;1996). The species is migratory. It breeds from April to July in solitary pairs in open grassland (Hayman et al. 1986, del Hoyo et al. 1996).
Threats and conservation measures listed
Threats listed in assessment
Within the UAE, the greatest threat to this species likely comes from changes in land-use but the severity of such threats are essentially unknown. Globally though, the species faces a range of threats which are driving its decline at the global level; and such threats may have an impact on individuals that visit the UAE: this species suffered past declines as a result of land-use intensification, wetland drainage and egg collecting (del Hoyo et al. 1996). Land-use intensification remains a problem: today it is threatened by reduced breeding productivity as a result of intensifying and changing agricultural practices (del Hoyo et al. 1996), especially the improvement of grasslands (e.g. by drainage, application of inorganic fertilizers and reseeding) (Baldi et al. 2005), increased growing of ""winter-crops"" (see Eggers et al. 2011), and loss of field margins and semi-natural habitat. Important migratory stop-over habitats for this species on the Baltic Sea coastline are threatened by petroleum pollution, wetland drainage for irrigation, land abandonment and changing land management practices leading to scrub overgrowth (Grishanov 2006). Clutch destruction may also occur during spring cultivation (using machinery) on arable fields (del Hoyo et al. 1996). The species is susceptible to avian botulism so may be threatened by future outbreaks of the disease (Hubalek et al. 2005). The species is hunted for commercial use (to be sold as food) and for recreational purposes in Iran (Balmaki and Barati 2006).
History
The species could have been assessed as CR for 1996, but would have been downlisted by one step to EN given the better global status at the time.
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