Curruca conspicillata
Curruca conspicillata
The Sardinian warbler has a distribution restricted to western Europe, where it is especially Mediterranean, occurs in northwest Africa, and also has populations in the Near East (Keller et al., 2020; BirdLife International, 2024). In Spain, it is distributed in a fragmented manner, with higher abundances in the Ebro Depression, the northern plateau, and the Central System, as well as along the Mediterranean coast from Cabo de la Nao to Gibraltar (Calleja and Pérez-Granados in SEO/BirdLife, 2022). It occurs in the Balearic Islands and in the Canary Islands as the subspecies orbitalis, endemic to the Macaronesian region (Trujillo in Lorenzo, 2007).
In the Community of Madrid, it appears in the central and northeastern areas, with its main nucleus in the grasslands of the mountain foothills, and scattered populations in the southern half. It prefers esparto grasslands and kermes oak scrubs in the south, and very open juniper groves in the northern half (Díaz et al., 1994).
In the national park, the highest abundances are found along the eastern portion of Cuerda Larga and around the Morcuera pass, in slope and grassland areas with some shrub substrate of broom and other shrubs in clearings, edges, and borders with forest stands. It is also located in high-altitude grassland areas with shrubby substrate in the northeastern end of the park, around Navafría pass and Reajo Alto.

It is a species that requires a shrub substrate, although it occupies a wide altitudinal range from coastal areas to high mountains. These shrub areas should be low-growing and not very dense, in communities dominated by gorse (Genista spp.), rockroses (Cistus spp., Halimium spp.), rosemary (Salvia rosmarinifolia), lavender (Lavandula spp.), thyme (Thymus spp.), or kermes oak (Quercus coccifera) (Calleja and Pérez-Granados in SEO/BirdLife, 2022). For reproduction, it uses open forest formations of junipers and savins (Juniperus spp.; Tellería et al., 1999), as well as mosaics with dryland plots with live hedges and abandoned plots with woody plants.
In the national park, it shows its highest densities mainly in areas with shrub substrate.

At the global scale, it is considered in the Least Concern category (LC; 2024). In Europe, it would also be classified in the same category (LC; 2020). In Spain, it is considered in the Least Concern category in the 2021 Red List.
The Catalogue of Threatened Species of the Community of Madrid (1992) does not consider the species in any threat category.
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.
Lorenzo, J. A. (ed.) 2007. Atlas de las aves nidificantes en el archipiélago canario (1997-2003). Dirección General de Conservación de la Naturaleza-Sociedad Española de Ornitología. Madrid.
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.