Taxon name
Passer domesticus
(Linnaeus, 1758)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Passer domesticus
(Linnaeus, 1758)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Species authority
(Linnaeus, 1758)
Taxonomic notes and synonyms listed
Passer domesticus and P. italiae (del Hoyo and Collar 2016) were previously lumped as P. domesticus following AERC TAC (2003); AOU (1998 and supplements); Christidis and Boles (2008); Cramp et al. (1977-1994); Dowsett and Forbes-Watson (1993); SACC (2005 and updates); Sibley and Monroe (1990, 1993); Stotz et al. (1996); Turbott (1990).
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)
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Least Concern
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species is thought to have an extremely large resident population size within the UAE, which is suspected to be increasing as it colonises new areas. Therefore, it is assessed here as Least Concern.
Assessment details
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
This species is an abundant resident; its range expanded rapidly since the 1980s and now spans the entire country (Jennings 2010, Pedersen et al. 2017). The earliest records of the species in the UAE are from the 1940s. In Abu Dhabi City, the species was not found until the 1970s, but was already regarded as common by 1980 (Jennings 2010). During the 1980s, it spread through Liwa (Abu Dhabi) and colonised several islands, including Das Island in the 1990s (Jennings 2010). The rapid expansion of the range and population are likely a consequence of the spread of irrigation, cultivation and urban developments in the country (Jennings 2010). Subspecies indicus occurs throughout the year in the UAE, but it is possible that several other subspecies from western and central Asia visit the country (Jennings 2010, Pedersen et al. 2017).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Habitat
Habitat details as listed in assessment
This species is often associated with man, living around buildings from isolated farms to villages and urban centres, though it also colonizes isolated areas far away from human population. It has been expanding its range in Arabia by using human developments like villages, farms, plantations or even petrol stops as dispersal corridors (Jennings 2010). The availability of water is crucial for the species (Jennings 2010). The diet is mainly vegetable material, particularly seeds of grasses and green shoots, cultivated cereals and low herbs, but also fruits, such as dates and berries, and wide range of household scraps (Summers-Smith et al. 2015). It also feeds on invertebrates, such as moths, caterpillars and ants (Jennings 2010). It forages mainly on the ground or in low vegetation. It shows a wide variety of foraging techniques, from hovering flights to pick items from leaves, to running and hopping or aerial pursuits in search for insect prey (Jennings 2010). It nests colonially, sometimes together with other species (e.g. Spanish Sparrow Passer hispaniolensis, although P. hispaniolensis is now possibly extinct as a breeding species within the UAE). Nests are constructed mainly of plant stems, lined with feathers or other soft material. They can be placed almost anywhere, e.g. in a hole in a building, in a cliff or in a tree (Jennings 2010, Summers-Smith et al. 2015). While breeding has been observed year-round, the main period lasts from May to June (Jennings 2010).
Threats and conservation measures listed
Threats listed in assessment
Declines in western Europe have been attributed to a decrease in availability of suitable invertebrate food necessary for rearing young as well as possible reduced fitness of those young that fledge successfully (Summers-Smith et al. 2015). This may be as a result of changes in agricultural practices such as the increased use of pesticides and herbicides and the autumn sowing of cereals, which have lead to decreases in food for this species (Hagemeijer and Blair 1997), although this is not thought to be a threat operating within the UAE. Indeed, Aspinall (1996) did not highlight any particular threats to the species within the country.
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