Abstract:The altitudinal distribution, breeding density and population size of Tengmalm’s Owl Aegolius funereus was studied in Kopaonik National Park (central Serbia) during the 2011 and 2012 breeding seasons. The size of the study area was 24 km2. The survey method applied was a line transect in combination with stop points and playback of territorial male call. During the two-year research project, 37 territories were located. In Kopaonik National Park, Tengmalm’s Owl males inhabit Norway Spruce Picea abies, mixed No… Show more
“…Across the European distribution range, both species are highly dependent on old growth (>80 years old), and primarily, coniferous forest stands, choosing dry and dead trees with cavities for breeding and food storage [ 45 ]. In Southern Europe, particularly on the Balkan Peninsula, both species prefer higher elevations, north-faced slopes, and medium-to-dense forests with a cold and humid climate [ 46 , 47 , 48 ]. Therefore, it can be assumed that Boreal and Eurasian Pygmy Owls are stenovalent habitat specialists with a narrow tolerance range and few possibilities of adaptation, which can only survive in the specific, above-mentioned environmental conditions.…”
Studying current and future geographic distribution is essential for conserving endangered species such as the Boreal Owl and Eurasian Pygmy Owl. The main aim of this study was to determine the potential distribution of both species in the Balkan Peninsula by using spatial distribution models (SDMs) in MaxEnt. We used data from field surveys, the scientific and grey literature, and an online database. We considered the current time and two future periods, 2041–2060 and 2061–2080. For future periods, we included different climate scenarios (SSP 126, 245, 370, and 585) in studying the potential geographic distribution of both species. We identified two types of potential future refugia for species: in situ and ex situ. Our study shows the highly suitable area for the Boreal Owl increased during the 2041–2060 period compared with the current area in all scenarios, except in SSP 585. However, during the 2061–2080 period, the highly suitable areas contracted. For the Eurasian Pygmy Owl, highly suitable areas decreased during 2041–2060, but during the 2061–2080 period, it was larger than the current area. Our study is of importance for conservation and preserving areas of potential distribution and refugia for Boreal and Eurasian Pygmy Owls in the face of climate change.
“…Across the European distribution range, both species are highly dependent on old growth (>80 years old), and primarily, coniferous forest stands, choosing dry and dead trees with cavities for breeding and food storage [ 45 ]. In Southern Europe, particularly on the Balkan Peninsula, both species prefer higher elevations, north-faced slopes, and medium-to-dense forests with a cold and humid climate [ 46 , 47 , 48 ]. Therefore, it can be assumed that Boreal and Eurasian Pygmy Owls are stenovalent habitat specialists with a narrow tolerance range and few possibilities of adaptation, which can only survive in the specific, above-mentioned environmental conditions.…”
Studying current and future geographic distribution is essential for conserving endangered species such as the Boreal Owl and Eurasian Pygmy Owl. The main aim of this study was to determine the potential distribution of both species in the Balkan Peninsula by using spatial distribution models (SDMs) in MaxEnt. We used data from field surveys, the scientific and grey literature, and an online database. We considered the current time and two future periods, 2041–2060 and 2061–2080. For future periods, we included different climate scenarios (SSP 126, 245, 370, and 585) in studying the potential geographic distribution of both species. We identified two types of potential future refugia for species: in situ and ex situ. Our study shows the highly suitable area for the Boreal Owl increased during the 2041–2060 period compared with the current area in all scenarios, except in SSP 585. However, during the 2061–2080 period, the highly suitable areas contracted. For the Eurasian Pygmy Owl, highly suitable areas decreased during 2041–2060, but during the 2061–2080 period, it was larger than the current area. Our study is of importance for conservation and preserving areas of potential distribution and refugia for Boreal and Eurasian Pygmy Owls in the face of climate change.
“…About 75% of the study area consists of high-mountain forests (mostly Norway spruce, Picea abies), 22% of open grassland-rocky terrain, and 3% of built-up areas. A detailed description of the study area can be found in earlier publications (Rajković et al, 2010(Rajković et al, , 2013.…”
The European continent represents a breeding area for 13 owl species (Mikkola, 1983). Their diet has been well documented for most species, especially in central and northern parts of the continent (e.g., Uttendörfer, 1952;Mikkola, 1983;Birrer, 2009). These diet studies were performed in various habitat types during different seasons and across dissimilar time spans. However, despite such a large number of studies, feeding habits of breeding owl species are still unknown for many vast regions (e.g., mountain ranges). One species that is relatively poorly investigated in such areas, particularly in southeastern and eastern Europe, is Tengmalm's owl Aegolius funereus, a small forest-dwelling predator, which occurs in the taiga forest belt across Eurasia and North America (Mikkola, 1983;König and Weick, 2008). In the Balkan Peninsula, the Tengmalm's owl population is regarded as a postglacial relict population (Simeonov et al., 1990). In Serbia, this rare nocturnal predator inhabits high mountain areas (>1000 m) covered with mixed and coniferous forests in the western and southwestern parts of the country (Rajković et al., 2010). Across the European continent, this owl species has been in the focus of numerous feeding ecology studies (e.g.
“…Average population density of the species in the Pirin NP was calculated at 9.6 territories/1000 ha of appropriate habitat which is comparatively high value. For comparison the same value at Kopaonik Mt., Central Serbia is 7.7 (Rajkovic et al 2013), at Krim Mt., Central Slovenia 2.8 (Vrezec 2003), in France 6-13 (Jonieniaux & Durand 1987), in W-Finland 0.1-2.6 (Korpimäki & Norrdahl 1989), in Sweden up to 4.8 in peak years (Kallander 1964).…”
Section: Population Numbers Trends Changes In the Distributionmentioning
confidence: 89%
“…Kopaonik, Central Serbia, and a density of 7.7 territories/1000 ha was reported. The species was found mostly in Norway Spruce forests (Rajkovic et al 2013). The distribution, biology and habitat requirements of the Pygmy Owl were studied in parts of Romanian Carpathians, where the population density was calculated at 6.1-7.3 pairs/1000 ha (Mestecaneanu & Mestecaneanu 2019).…”
Actual status, distribution, numbers and threats for four forest bird species -Tengmalm's Owl (Aegolius funereus), Pygmy Owl (Glaucidium passerinum), Three-toed Woodpecker (Picoides tridactylus), and Capercaillie (Tetrao urogallus) were studied in the territory of the Pirin National Park, Bulgaria, in the years 2001and 2019 For the owls, we used night line transect, 2-5 km in length, with acoustic imitation of species calls (henceforth playback) at each 500 (700) m (38 points in 2001-2002, 80 points in 2019). Daytime line transects, 2-5 km in length, were used for counting woodpeckers and Pygmy Owl. In Capercaillie counts, we searched for tracks in the snow, excrements or feathers. GIS analyses were applied for visualization of habitat association and distribution patterns of the studied species. The numbers and distribution of these species were compared between the two study periods and with existing data from previous studies. In 2019 a total of 29 occupied territories of Tengmalm's Owls, 20 territories of Pygmy Owls, 2 territories of Three-toed Woodpeckers and 16 leks of Capercaillies were found. Decrease in numbers was detected for Tengmalm's Owl (-30.4%) and Capercaillie. These species showed also different spatial pattern of presence between the two study periods. Three-toed Woodpecker population in Pirin NP is very small, not exceeding 10-15 pairs. Pygmy Owl was recorded for the first time during the breeding period in the National Park. The reasons for the differences between the two study periods were discussed. The results indicate some threats (ski tourism development, disturbance by people, sanitary cuttings, etc.) for these birds and can be used for improving the spatial planning of human activities in Pirin NP.
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