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For the study 19 roebucks of the same age (1-3 years), shot in May 1960 and 1990 in Rogów, were used. During this thirty year period, many changes took place in the density of the roe deer population and in the manner of their taking, as well as in the species composition of cervids living together. The list of species of nematodes found in roe deer in this territory was enriched in 1990 with Ostertagia antipini and Spiculopteragia dagestanica, typical parasites of elk. Increase of the red deer population in the forests of Rogów did not influence the nematode fauna of the abomasum of roe deer in this hunting ground. However, the high increase of roe deer density in Rogów in 1990 (area B), as compared with 1960, significantly influenced the prevalence of infection with Trichostrongylus axei, T. capricola and Haemonchus contortus. The differences between mean intensities of infection of particular nematode species from the subfamily Ostertagiinae in 1960 and 1990 were insignificant. A distinct influence on the intensity of infection of many nematode species was exerted by the manner of taking roe deer, considerably different in area A and В (1990). In strongly exploited area A, the intensity of T. axei, T. capricola and H. contortus considerably decreased. This concerned especially the mean intensity of infection with H. contortus, which decreased in area A by forty-two times in comparison with area B.
From 1991 to 1995, wolf Canis lupus (Linnaeus, 1758} population dynamics were studied in Bieszczady National Park and the surrounding area (520 km2). The study area was utilized by 5 packs, Pack sizes averaged 5.6 in early and 3.9 in late winter. Overwinter declines in wolf numbers ranged from 21% to 39% (x = 29%), which corresponded well to the known number of wolves killed by hunters or dead of other causes. After every winter decline, wolf numbers recovered through reproduction. Generally, wolf numbers were stable or slightly decreasing during the study. Three neighbouring wojf packs occupied an area of 340 km" and the estimated territory size averaged 85 km2. The estimated density of wolves averaged 5,1/100 km2 in early winter and 3.3/100 km' in late winter. Of all known causes of wolf mortality, 86% were from legal hunting, 5% were from poaching, and 9% were from natural causes. Bieszczady National Park is small in size and its topography influences the spatial distribution of packs. No single pack was fully contained within, or protected by the Park. The number of wolves is overestimated in official reports, because the same packs are likely counted as different groups in neighbouring census units. On hunting grounds adjacent to Bieszczady NP, harvest plans exceed the actual number of wolves which inhabit the area. The creation of a wolf protection zone around Bieszczady NP and some regulations for wolf management in the rest of the region are proposed.
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