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Back to Wolves and Humans Homepage Wolves in Poland 2 Poland - one of the biggest countries of central Europe (312,685 km ) is inhabited by almost 40 million people. Large wood complexes of pine, spruce, mixed and deciduous (consisting of beech, hornbeam, birch, oak, lime, maple) forests, rich in native species of plants and animals, cover about 28% of the total country area. 89 % of forests are public forests and are managed by the State Forest Service. The ungulate community consists mostly of four native species: red deer, roe deer, wild boar and moose. In a few places small isolated free-ranging populations of European bison still exist. The population of three main ungulate species has increased significantly during the last forty years and in 2000 reached a level of 117,500 red deer, 597,000 roe deer, 180,300 wild boar (the moose population is still small, about 2,000 individuals and slightly decreasing) in the whole of Poland. Ungulates cause large scale damage to young trees plantations and thickets and cost of prevention activities in the State Forests achieved a peak of £12 million. Such circumstances create ideal conditions for the large predators present. The large carnivore community includes the wolf, the lynx and the brown bear in Poland. All these species are protected in the whole country, the brown bear since 1957, the lynx since 1995, and the wolf since 1998. The only region inhabited by brown bear is the Carpathian Mts. (south east and south central Poland), where no more than 80 individuals occur. They are part of a larger population inhabiting the Carpathian Mountain range. Lynx is not a common species in Poland. Its distribution is limited to north-eastern and, eastern part of Poland and the Carpathian Mts. According to preliminary results of this year’s large scale inventory of wolf and lynx populations, the number of lynx is surprisingly low, about 180 individuals. Wolf distribution and numbers in Poland The wolf is a species relatively more widespread in Poland than brown bear and lynx. The majority of the Polish wolf population is a vital part of a continuous Eastern Europe wolf population and inhabits north-eastern, eastern and southern (Carpathian Mts) part of our country. Isolated populations in the large forest complexes of Western Poland, near German-Polish border comprise only a few individuals. According to the inventory mentioned above, the number of wolf packs is estimated at about 110, and the total number of wolves at about 500 individuals. These estimates are half the number of last year’s official data, which was based on hunter's inventories. Studies on wolves in Poland The biggest refuge for Polish wolves is the Carpathian Mts. (Bieszczady Mts., Tatra Mts. and he Beskidy Mts.) together with the Carpathian foothills, which is home to about 200 individuals. This population is partly shared with Slovakia and Ukraine. The other main wolf areas are the large forest complexes of north-eastern Poland (Białowieża Primeval Forest, Augustowska Forest, Knyszyńska Forest, Piska Forest), where about 160-190 wolves occur, although some wolf packs have territories on Belarusia and Russia side as well. Regular studies on wolves have been conducted in Poland for about fifteen years, mainly in Białowieża Primeval Forest and in the Bieszczady Mountains, the most natural forests complexes in our country. This gave an opportunity to research the correlation between predators and prey in quite natural conditions, with very little human impact. Currently, studies on wolf populations are conducted in the Western Beskidy Mountains, the Piska Forest (NE Poland), and in the Bieszczady Mountains (telemetry) as well. The results of latest surveys are still preliminary, but they give some answers on the impact of wolves on the managed forests. Ecology of wolves in Poland According to these studies the average number of wolves in a pack varies from to 3-5 individuals. The wolf pack territory covers about 200-300 km2 in lowland (Okarma et al. 1998b) and about 100 km2 in the mountains (Śmietana and Wajda 1997, Nowak and Mysłajek unpubl.), and depends on the local density of ungulates and the land shape. For example the average density of wolves in the Białowieża Primeval Forest, where the number of wild prey is relatively high, is about 2-3 individuals/100 km2, for the Bieszczady Mts. the wolf density reaches 4.2 individuals/100 km2, and is the biggest in Poland. Wolves in Poland mostly prey on wild ungulates. The local ungulate community structure depends on the predominant kind of management in the forest complex. The majority of Polish forests are exploited forests and in such areas the ungulate community consists of 60-80% roe deer, 15% red deer, 5-20% wild boar and others. Polish studies on wolf diet reported that wolves prefer to prey on red deer, which composed about 40-55% of all kills by these predators and about 70-80% of biomass of consumed food (Jędrzejewski et al. 1992, Śmietana and Klimek 1993, Nowak and Mysłajek unpubl.). Roe deer and wild boar are quite important, but depend on local conditions and season, source of food, and their contribution to the wolf diet is smaller than can be expected based on the local ungulate structure. According to studies in Białowieża Primeval Forest, during one week a wolf pack kills about 3 ungulates. The average daily consumption is about 4-7 kilos per wolf. Kills are eaten very fast; one medium pack can consume an adult female red deer in 1½ days. Every year wolves remove about 15% of individuals from the red deer population and about 5% of individuals from the roe deer population (Jędrzejewski et al. 2000). Whilst access to food sources seems to be the main factor that limits the local ungulate density, the wolves can significantly influence ungulate numbers and the rate of growth of red deer and roe deer in the forest complex. The occurrence of wolves in the forest complex can decrease the density of red deer and partly roe deer. Wolves restrict the rate of growth of red deer and roe deer populations and prevent the maximum densities of ungulates allowed by food resources being reached. This influence is highly positive, preventing overdensity and competition for food resulting in poor condition and vulnerability to different diseases. To achieve an overview of the impact of wolf predation on the ungulate community, the age and sex structure of kills were analysed, based on prey remains and wolf scats. According to study in Białowieża Primeval Forest the most frequent prey amongst red deer were calves (61%) and then adult females (31%) (Jędrzejewski et al. 1992). Only 14-27% of kills consisted of red deer males (Okarma et. al. 1995). In the wild boar population the percentage of killed youngsters was even bigger and reached 94% (Jędrzejewski et al. 1992). Such selective predation was not found with respect to the roe deer population. Practically, wolves were killing roe deer nonselectively in every age and sex (Okarma et al. 1995). The remains of prey found in the Bieszczady Mts. showed that wolves killed mostly red deer females (40-45%) and calves (32-51%) and rarely males (9-24%) (Okarma 1991, Bobek et al. 1992). Amongst males the young individuals were killed more frequently and than very old ones. In total, amongst 61 prey remains found 57% consisted of calves and young individuals aged below three years (Bobek et al. 1992). Scat analysis showed that in the Bieszczady Mts amongst wild boars the most frequent wolf kills (76%) were youngsters (Śmietana and Klimek 1993). Main threats to wolf population in Poland Damages to livestock caused by wolves In addition to wild ungulates, wolves prey on livestock in almost the whole range of their distribution in Poland. Some packs more frequently, some incidentally. The level of damages depends on local densities of wild predators (Jędrzejewska & Jędrzejewski 1998), areas inhabited by packs and prevention methods used by farmers. Every year the distribution of damages across the country changes, and varies between £24,000 - £27 000. According to Polish law, losses are compensated by the State, but the system of estimating damages and the payment procedure needs to be improved. Despite compensation payments, wolf predation on livestock causes affected farmers to try to force the return of the wolf to the game list or at least the removal of wolf packs from neighbouring areas. This is strongly supported by hunters, who still see wolf predation on wild ungulates as a similar kind of loss, and present an influential force of 100,000 members of the Polish Hunting Union. Over hunting of wild ungulates in wolf areas From the other side, hunting plans do not take into account the feeding needs of large carnivores inhabiting forests areas. This results in decreasing local wild prey populations and increasing losses amongst domestic animals, and conflicts with livestock owners Wolf killing in trans-border areas. Most of the neighbouring countries, which share the same wolf population with Poland, in spite of being signatories to the Bern Convention, have not developed similar protection laws towards this species. Wolves are killed as a game species in Slovak Republic, and are regularly persecuted in Ukraine, Belarus and Russia. Wolf killing causes instability of trans-border wolf populations in the Carpathian Mountains (in the Polish part of Carpathians, too) and in the eastern part of Poland. In the last few years in spite of laws protecting them in the Czech Republic and Germany, several roaming wolves from Poland were shot by hunters, near the Polish border (Nowak & Mysłajek 2001). Poaching. According to studies in the Białowieża Primeval Forest the illegal killing and snaring (not only of wolves but also wild ungulates) causes about 20% of mortality among wolves, in eastern Poland. This problem is much lower in the rest of Poland, where poaching is not so frequent. The next important threat is taking of pups from dens, temporarily (to show to family or to take a picture) or permanently to breed (rear) or to cross with dogs. Such cases are not rare in forest complexes intensively penetrated by people. People are still not aware of the consequences of such activities (Nowak & Mysłajek 1999, 2001). Foresters activity and human penetration According to the current model of forest management in Poland, foresters work such as weed cutting, thicket cleaning, thinning, tree clearance or even logging lasts throughout the year, and disturbs wolves during the denning season and the pups rearing. The traditional, annual intensive penetration of woods by people is limited to the late summer and early autumn months of the mushroom crop, but force wolves to frequently change resting places with pups and this can influence rearing success as well. Lack of corridors between forest complexes, fragmentation of existing forests by highway construction and development of motor traffic. In spite of strict protection of this species in the whole of Poland, a dramatic decrease in wolf numbers in western Poland has been recorded during the last few years (from about 40 individuals to just 13). This suggests a lack of roaming wolves to enrich these isolated local small populations with new individuals. Such migration would be a source of animals, which are crucial in cases of death of local wolves from disease and parasites such as mange, car accidents, injures and accidental poaching. It shows the importance of contact of wolves in western Poland with the core population in eastern and southern Poland. The lack of roaming wolves could be a result of the breaking of old migration routes by the rapid development of motor traffic and motorways during the last ten years in Poland. From the other side the interim results of this year’s inventory suggests that still not all forest complexes in eastern, northern and southern parts of Poland are inhabited by wolves and the densities are not high enough to promote the long migration of young individuals to the west. Also the migration routes through wide, deep rivers like the Wisła can be limited to cold winters when the river is covered by thick ice. Activities for long-term wolf protection in Poland It is impossible to protect wolves through establishing special protected areas for them. It is important to allow wolves to inhabit all suitable managed forests and to increase acceptance of these predators amongst local communities, mostly farmers, foresters and hunters. This is the reason why widespread education and intensive monitoring as well as resolving conflicts between man/wolf are fundamental to work for the long-term protection of wolves. There are several initiatives, which were developed and carried out for the benefit of wolves by the Association for Nature WOLF in Poland (Mysłajek & Nowak 1998, Nowak & Mysłajek 1999, 2001). The National Strategy of Wolf Protection and Management Association for Nature WOLF was calling for the development of this strategy, for several years. In 1998 a group of wolf specialists (including a representative of AfN) developed and submitted this project to the Ministry of Environment (Okarma et al. 1998). The Strategy includes: a consistent protection system for the wolf throughout the whole country, mostly in large forest complexes; a wolf habitat protection programme; an improved, efficient system of compensation for livestock damages caused by wolves; a training and consulting program concerning prevention methods for farmers (e.g. guarding dogs and mobile fences); rules for removal of wolves specialised in preying on livestock from areas of greatest conflicts; development of a scientific research programme concerning wolf populations in Poland and large-scale monitoring; and a widespread education programme for the general public. This strategy has been approved by the State Nature Protection Council. Wolf monitoring and study Because the previous studies on wolves in Poland were conducted in forest complexes, which are in mostly protected as national parks and nature reserves and are rarely populated, our association decided in 1996 to start its own study project on dynamics, ecology, and conservation problems of wolf populations in the Western Beskidy Mountains (about 745 km2, mainly managed forest). Our goal is to recognise the mechanism of adaptation of wolves to conditions of high human penetration and forestry activity, which are common in existing wolf territories and in potential areas for wolf recolonisation in our country. During our study we have found the wolf distribution and abundance, the approximate dimensions of wolf territories, the wolf diet, breeding success, the influence of wolf predation on the local ungulates and livestock, the main threats and conflicts between wolves and humans. The previous official data on wolf and lynx occurrence and numbers in the whole Poland were based solely on hunter's inventories. Currently a large-scale inventory of wolf and lynx populations is conducted in all forest divisions in Poland, in close co-operation with foresters from all forest divisions. The aim is to recognise the distribution and abundance of both species, as well as existing barriers for spontaneous migration. This project is co-ordinated by the Mammal Research Institute of the Polish Academy of Science in Białowieża and the Association for Nature WOLF. In addition to the verification of data on wolf and lynx occurrence, and wolf pack numbers in Poland, basic education and training of Polish foresters also takes place. Furthermore, to locate all wolf packs, which inhabited trans-border areas of Poland and Germany, members of AfN WOLF conduct detailed surveys, including summer howling sessions, in co-operation with German environmentalists. The aim is to identify actual wolf key areas and potential sites providing suitable habitat for these animals, with special focus on their potential to support the reestablishment of wolf population in Germany. The next aim is to recognise the main threats and develop local wolf protection plans. Wide education of society in Poland and abroad. Since 1996 AfN WOLF has organised dozens of talks, lectures and wolf workshops for school children, students, teachers, journalists, foresters, staff of Nature Protection Departments, National and Landscape Parks, local authorities and others. More than 4,200 people have been educated this way. Several educational booklets, posters, stickers, T-shirts, and two guidebooks have been published. Resolving conflicts between farmers and wolves. Currently two projects for livestock owners are conducted in Poland. In the Bieszczady Mountains, a project to introduce and train Tatra Mountain Shepherd Dogs for protection of sheep flocks. This project is co-ordinated by Dr Wojciech Śmietana from the Institute of Nature Conservation PAS. In the Western Beskidy Mountains, AfN WOLF in co-operation with Landscape Parks conducts a project to educate local farmers and equip them with mobile fences called "fladry". Also shepherd dogs will be introduced to this project, next year (Nowak & Mysłajek 2001). References Bobek B., Perzanowski K., Śmietana W. 1992. The influence of snow cover on wolf Canis lupus and red deer Cervus elaphus relationships in Bieszczady Mountains. In: Global trends in wildlife management (Bobek B., Perzanowski K. & Regelin W. Świat Press, Kraków-Warszawa: 341-348. Jędrzejewska B., Jędrzejewski W. 1998. Predation in vertebrate communities. The Białowieża Primeval Forest as a case study. Springer-Verlag, Ecological Studies 135. Berlin - Heidelberg - New York. 1-450. Jędrzejewski W., Jędrzejewska B., Okarma H., Ruprecht A.L. 1992. Wolf predation and snov cover as mortality factors in the ungulate community of the Białowieża Primeval Forest. Oecologia 90: 27-36. Jędrzejewski W., Jędrzejewska B., Okarma H., Schmidt K., Zub K. and Musiani M. 2000. Prey selection and predation by wolves in Białowieża Primeval Forest, Poland. Journal of Mammalogy 81: 197-212. Mysłajek R.W., Nowak S. 1998. Wolf protection in the Polish part of the Carpathians – an example of the activities of the Association for Nature „WOLF”. International Scientific-Practical Conference „Issues of sustainable development in the Carpathian Region”, Rakhiv, Ukraine, 13-15.10.1998. Proc. Vol. 2: 106-111. Nowak S., Mysłajek R.W. 1999. Conservations problems of the wolf Canis lupus in Poland. Przegląd Przyrodniczy 10, ¾: 163172 [in Polish with English abstract]. Nowak S., Mysłajek R.W. 2001. Problems of Wolf Protection in Poland. Canid Biology and Conservation Conference, Oxford, Wielka Brytania, 17-21.09.2001r. Programme & Abstracts: 87. Okarma H. 1991. Marrow fat content, sex and age of red deer killed by wolves in winter in the Carpathian Mountains. Holarctic Ecology 14: 169-172. Okarma H. 1995. The trophic ecology of wolves and their predatory role in ungulate communites of forest ecosystems in Europe. Acta Theriologica 40: 335-386. Okarma H., Jędrzejewski W., Jędrzejewska B., Nowak S., Śmietana W. 1998a. [The Strategy of Wolf Protection and Management in Poland]. IOP PAN, Kraków: 1-38 [in Polish]. Okarma H., Jędrzejewski W., Schmidt K., Śnieżko S., Bunevich A. N., Jędrzejewska B. 1998b. Home ranges of wolves in Białowieża Primeval Forest, Poland, compared with other Eurasian populations. Journal of Mammalogy 79: 842-852. Śmietana W., Wajda J. 1993. Diet of wolves in the Bieszczady Mountains, Poland. Acta Theriologica 38: 245-251. © Association for Nature “WOLF” and The Wolves and Humans Foundation 2005. Unauthorised reproduction of all or part of this document is prohibited.