Eurasian Wren

Troglodytes troglodytes

More information on other websites:

Eurasian Wren

Troglodytes troglodytes

More information on other websites:

Distribution

The Eurasian wren has a disjunct distribution between Asia and Europe (BirdLife International, 2024). In Europe, it occupies the entire continent except for the coldest areas north of Fennoscandia (Keller et al., 2020). In Spain, it is distributed continuously across the northern half of the Iberian Peninsula, except in deforested areas of the Ebro Valley and the northern Meseta. In the southern half, its distribution is more fragmented, occurring continuously only in the mountain systems of Sierra Morena and the Baetic Range (Justo Álvarez and Torralvo Moreno in SEO/BirdLife, 2022). It breeds in the Balearic Islands and Ceuta, but is absent from the Canary Islands and Melilla.

In Madrid, it occupies the entire mountain range and piedmont belt, extending into the southeastern half via riparian woodlands. It prefers forested environments, especially cool habitats such as ash groves, Scots pine forests, and oak woods. It can also be found in riparian stands and gardens, provided there is abundant shrub cover, and it is not uncommon in high-mountain shrublands such as broom and heather thickets (Díaz et al., 1994).

In the national park it is very widely distributed, with notable presence in the central and southern areas of the protected space, as well as on the slopes and high zones of the northern sector, where it finds suitable breeding habitats in forest stands and in high-mountain shrublands dominated by broom.

 

Habitat

This species requires a humid and cool environment, so it is more abundant in forested areas of the northern third of the peninsula and in mountainous regions. It occupies a wide variety of forest habitats as long as there is abundant shrub vegetation (Tellería et al., 1999). It also inhabits urban parks and gardens.

Within the national park, its highest densities occur in forested stands of pinewoods with understory, as well as in oak woods and mixed broadleaf formations. It also reaches important densities in shrub-dominated areas, especially in high-mountain broomlands, which are heavily used by this species for breeding in the park. It is absent or reaches only minimal densities in high-mountain grasslands lacking broom.

Conservation status

Globally, it is classified as Least Concern (LC; 2018). In Europe it is also listed under the same category (LC; 2020). In Spain, it is considered Least Concern in the 2021 Red List.

The Red List of Threatened Species of the Community of Madrid (1992) does not include this species in any threat category.

Bibliography

BirdLife International 2024. IUCN Red List for birds. https://datazone.birdlife.org.

Díaz, M., Martí, R., Gómez-Manzaneque, Á. y Sánchez, A. 1994. Atlas de las aves nidificantes en Madrid. Agencia de Medio Ambiente y SEO/BirdLife. Madrid.

Keller, V., Herrando, S., Voříšek, P., Franch, M., Kipson, M., Milanesi, P., Martí, D., Antón, M., Klvaňová, A., Kalyakin, M. V. Bauer, H. Gr y Foppen, R. P. B. 2020. European Breeding Bird Atlas 2: Distribution, Abundance and Change. European Birds Census Council y Lynx Edicions. Barcelona.

SEO/BirdLife (Molina, B., Nebreda, A., Muñoz, A. R., Seoane, J., Real, R., Bustamante, J. y Del Moral, J. C., eds.). 2022. III Atlas de las aves en época de reproducción en España. SEO/BirdLife. Madrid.

Tellería, J. L., Asensio, B. y, Díaz, M. 1999. Aves Ibéricas. II. Paseriformes. J. M. Reyero Editor. Madrid.