Most of the inhabitiants of Krkonoše made their living by agriculture, brought by the colonists from the Alps in the second half of the 16th century. A demanding climate and low fertility of the soils did not make possible a cultivation of many products in higher altitudes. The local inhabitants were dependent on animal husbandry, and the animals fed mostly on hay. This commodity was of crucial importance for the inhibitants of Krkonoše and influenced, among others, their economic activities, the way of management of grasslands, and also the landscape.
We studied the location of Eurasian badger (Meles meles) setts in relation to various environmental factors, and attempted to assess the role of competition with other burrowing carnivores and the importance of human activity on their sett selection in the Western Carpathians (southern Poland). Excavated dens (53 %), caves and rock crevices (43 %), and burrows under buildings (4 %), were used by badgers as permanent shelters. Setts were located mostly in foothills (< 680 m a.s.l.), but selection for den location within the lower montane zone (680-980 m a.s.l.) was also observed. Excavated setts were recorded only up to 640 m a.s.l., while setts in rock crevices occurred up to 1050 m a.s.l. Badger shelters were mainly situated in forests or covered by dense bushes. Badgers avoided northern slopes in all altitudinal zones, and located their burrows mostly on SE or W slopes in foothills, and S or E slopes in montane zones. Setts were placed further from human settlements and main roads, but closer to meadows with high earthworm biomass, when compared with random points. Within badger territories, 1-12 setts were recorded. Badgers occupying territories which included both foothills and montane zones used burrows at various altitudes, but their main setts used for overwintering, were located exclusively above 800 m a.s.l. We conclude that sett location by badgers in mountains is shaped not only by the availability of cover and geological factors influencing digging, but also by human pressure and distance to foraging areas.
Microtus tatricus occurs in the Carpathian Mountains of Slovakia, Poland, Ukraine and Romania – a list of current distribution records is given. The species’ distribution range is insular on the scale of its entire distribution and fragmented within each mountain range inhabited. The overall altitudinal range is 650–2350 m a.s.l., with the largest number of collecting sites situated between 1100–1700 m a.s.l. The total range size of M. tatricus was estimated as 840 km2 and the total population size at between 200,000–250,000 individuals. A possible reduction in the species’ distribution range is discussed.
Large-scale forest dieback was reported in recent decades in many parts of the world. In Slovakia, the most endangered species is Norway spruce (Picea Abies). Spruce dieback affects also indigenous mountain forests. We analysed changes in snow cover characteristics in the disturbed spruce forest representing the tree line zone (1420 m a.s.l.) in the Western Tatra Mountains, Slovakia, in five winter seasons 2013–2017. Snow depth, density and water equivalent (SWE) were measured biweekly (10–12 times per winter) at four sites representing the living forest (Living), disturbed forest with dead trees (Dead), forest opening (Open) and large open area outside the forest (Meadow). The data confirmed statistically significant differences in snow depth between the living and disturbed forest. These differences increased since the third winter after forest dieback. The differences in snow density between the disturbed and living forest were in most cases not significant. Variability of snow density expressed by coefficient of variation was approximately half that of the snow depth. Forest dieback resulted in a significant increase (about 25%) of the water amount stored in the snow while the snowmelt characteristics (snowmelt beginning and time of snow disappearance) did not change much. Average SWE calculated for all measurements conducted during five winters increased in the sequence Living < Dead < Meadow < Open. SWE variability expressed by the coefficient of variation increased in the opposite order.