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W latach 1992-1995 badaliśmy wpływ daty przylotu i wieku samca muchołówki białoszyjej Ficedula albicollis (wtórny dziuplak, zimujący w Afryce) na jakość miejsca lęgowego. Dane zbierano w grądach Białowieskiego Parku Narodowego od połowy kwietnia do ok. 20 maja. Za datę przylotu uznano dzień, w którym po raz pierwszy zaobserwowano śpiewającego i wchodzącego do dziupli samca. Wśród samców, na podstawie upierzenia, wyróżniono dwie grupy: młode (jednoroczne) i stare (dwuletnie i starsze). Za jakość dziupli przyjęto jej parametry (wysokość nad ziemią, wielkość otworu wlotowego, głębokość i powierzchnię dna). Określono terminy przylotów 216 samców oraz zmierzono ponad 300 dziupli. Młode samce przylatywały średnio 4 dni później (tab. 1, ryc. 1), mimo to jakość wybranych przez nie miejsc gniazdowych nie różniła się. Również korelacja między datą przylotu a poszczególnymi parametrami dziupli była statystycznie nieistotna (tab. 2 i 3). Świadczy to o nadmiarze dobrych miejsc gniazdowych i braku ostrej konkurencji o dziuple w grądach naturalnych Białowieskiego Parku Narodowego.
Cavities are important, natural components of forest ecosystems, conditioning the high level of biodiversity. They are formed either as a result of a natural process of wood decay caused by fungi or as excavations made by woodpeckers Picidae. Distribution and density of cavity trees are regionally diversified and dependent on species composition and age of the stands as well as the management way. In the global scale, decay cavities are much more numerous than those created by woodpeckers. Natural cavities dominated in deciduous forests, whilst woodpeckers−made ones – in coniferous stands. The density of cavities increases along the age gradient due to the growing size of trees and their worse health condition. Cavities in natural forests are more numerous than in commercial, managed ones. This is caused by the removal during the thinning of trees reduced in health, attacked by insects, fungi or mechanically damaged, which are potential places for the creation of cavities. The other reason is a too low age of the final cutting. Moreover, in the managed forest, cavity trees are often removed during sanitary cuttings, although leaving them is recommended. In European forests, the density of cavities is from less than 1 to almost 100 per ha. Natural cavities dominated in most of the studied plots. In Poland, their density varied from less than 1 to 16 per ha. Cavities are habitats and breeding sites of many specialized species of animals from invertebrates to mammals, fungi, and plants. In Poland, cavities are used by about 40 bird species, about 20 mammal species, as well as several hundred species of insects. According to the Polish forestry regulations, trees with cavities should be left to natural destruction, but there are no detail recommendations how to search for such trees and what is their required density. The recommendation to leave cavity trees will not contribute to the increase in their number in managed forests, unless one provides wider availability of adequately large trees with a reduced condition. In Polish forests, actions should be taken to increase the number of potential trees, in which cavities may be formed. They should be designed at the stage of tending for young stands. The minimal density of cavities in managed forests should be in the range of 1−3 per ha in coniferous and mixed forests up to 100 years old and above 3−4 per ha in stands older than 100 years, while in deciduous forests these values should equal to 2−5 per ha and 4−6 per ha in younger and older stands respectively.
Three species of cavity nesters potentially competitive with the Starling — the Great Spotted Woodpecker Dendrocopos major, Middle Spotted Woodpecker D. medius and Nuthatch Sitta europaea were studied in the years 1997-1999. The number of suitable nest sites for Starlings and competitive pressure were manipulated by increasing or decreasing the availability of nest boxes. Increased nest-site competition did not lead to significant changes in number among the studied species. The Starling was found to take over up to 25% of holes chosen by Nuthatches for breeding. Increased availability of nest sites did not protect Nuthatches from cavity losses, but reduced their frequency. Only 20% of Nuthatch pairs that lost their holes renested successfully in the same breeding season. No impact of Starlings on breeding woodpeckers was noted.
It is generally accepted that hole-nesting birds have a higher breeding success than open nesters. However, this group of birds can also experience frequent nesting failures, with the majority of them related to predation. This suggests that the attributes of some holes could make them safer than others. Several features of holes as nest sites could be considered in relation to predator pressure. Some of them influence the probability of predators finding the hole, while others describe the accessibility to eggs or nestlings (Fig. 1). Investigations of birds’ breeding success in relation to nest hole characteristics focused mostly on hole dimensions, such as entrance size or distance from the entrance to eggs/nestlings (the so-called „danger distance”) but in many such studies, no significant relations were found (Table I). In this article, special attention is paid to other hole features that may affect predation, but are relatively rarely considered in this respect - hole age and its utilization by birds in previous seasons. It seems that increasing hole age enhances predation pressure both due to the long-term memory of some predators (such as the Pine Marten), as well as changes in hole dimensions and wood hardness. Also, the material of old nests accumulates in holes used by birds over many seasons, and this may cause higher predation because the danger distance decreases (Fig. 2). Additionally, the large number of ectoparasites in such holes may influence adult and nestling behavior, which could attract predators. However, only a few studies address the issues of hole-nesting birds’ breeding and the problems related to hole age. Moreover, their results are inconsistent. When considering the breeding success of hole-nesting birds in relation to hole characteristics, it should be remembered that predation is a strong selective pressure, and birds endeavor to minimize the probability of nesting failure. This articles describes in detail the methods used by birds to avoid predator pressure that could be related to increasing hole age. They include selection of specific sites, avoidance of older holes or sites with old nests, site preparation by removing old nest material and adjustment of the new nest to the holes depth. Unfortunately, the relation between hole age or its previous utilization by birds and predator pressure, as well as birds’ behavioral responses to avoid predation, have still not been sufficiently studied.
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