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LIVESTOCK AND LARGE CARNIVORES IN PIATRA CRAIULUI
The report
presents different types of actions that aim to ensure the long term
conservation of large carnivores in Piatra Craiului area. Main actions are:
lobby and stakeholders consultations, electric fencing of local shepherd camps,
livestock depredation monitoring, ecological camps, information and public
awareness. The activities were carried out by using an integrated approach
focused on prevention and mitigation of possible conflicts between wolves,
bears and lynxes and livestock breeding activities. The specific results of
each action were integrated in a set of conclusions that was used for the
elaboration of the guidelines for large carnivore management in
Keywords livestock, electric fences, grazing, depredation, large carnivores.
The field survey report is based on five years of field activities done in Piatra Craiului area and related to large carnivores management and livestock depredation, as a major source of possible conflicts between human activities and wolves, bears and lynxes from the area.
This study was carried out in the frame of the LIFE Nature project "Enhancement of Piatra Craiului National Park" (LIFE Nature 99/ANT/RO/006435, time period 1999 - 2004) financed by European Union through the LIFE program. The project aims to integrate large carnivores management in the local context, by active involvement of local communities in nature and protected areas issues. The mitigation campaign was launched taking into account the existing situation from the area, where there are significant grazing activities in an area populated by large carnivores, a situation which occurs in many other locations in Romanian Carpathians.
In the
The traditional way of life, as grazing, mowing and even the logging are maintained and this have to continue in the future because a part of the natural environment evolved along the time under its influence and the unexpected end of these activities could lead to landscape change and decreasing the number of species from park and vicinity.
The hunting is one of the traditional activities, but in the last years was prohibited inside the park area. Still there are poaching activities that affect the game species, especially chamois, within the park borders. In the last ten years, the rural tourism was a successful activity, being about to become a significant source of income in the park area (Magura, Pestera, Dambovicioara and Moeciu villages).
One of the main activity in the park is grazing on pastures and alpine meadows (photo 1), which last from hundred of years of coexistence with large carnivores. In the last period, the intensive grazing activities on park alpine meadows had influenced both the habitats and wildlife species from the area.
The general objective of the survey was the implementation of modern measures to protect the livestock, measures that could contribute to a significant decreased of conflicts with large carnivore and to decreasing of alpine habitats degradation.
Photo 1. Southern grazing areas in
Photo 2. Traditional way of life preserved from centuries
Photo 4. Livestock night resting places, soil erosion and large carnivore habitats
Photo 3. Electric fence with solar panel
Photo 5. Shepherds and volunteers installing electric fences
Activities undertaken
The activities carried out in the park area were focused on large carnivore damages, implementation of new protection methods against large carnivore attacks, flora and soil impact reducing by rotation of night enclosures (photo 4), identifying grazing routes that have a significant impact on erosion, public awareness campaign regarding conflict mitigation and conservation support, support for sustainable use of local natural resources, pastures amelioration through allowed measures and support for future implementation of wildlife management plans in the area.
The stakeholders information and regular
consultations were done by contacting the sheepfold chiefs, the forest and
hunting units managers and the local councils and farmers. The main results of
this action are related to a database of grazing activities (persons, number of
livestock, grazing areas, surface of pastures, etc.), gaining support from
informed local stakeholders and grazing agreements signed with Dambovicioara and Moeciu communes that own
the pastures form
The implementation of livestock protection methods was done by installing mobile electric fences at the shepherd camps within the park area (photo 3). Thus, in March 2003 it was organized a Training Workshop for Electric Fences Use (24 participants from local and regional level) and in the next months there were signed custody agreements with the sheepfold chiefs from the park area. In 2003 were installed 7 electric fences at the shepherd camps within the park border and in 2004 were installed 5 electric fences. Other electric fences were installed for protection of crops and orchards against bear attacks, as a part of conflict mitigation campaign carried out in the park area.
Monitoring activities included data collection (number of livestock, grazing areas and routes, grazing conditions, damages caused by large carnivores). An important part of monitoring activities was related to help the local shepherd for regularly move of the night enclosure, in order to avoid soil degradation and proper livestock protection of electric fencing systems.
The information and conflict mitigation campaign was based on direct meetings and regular contacts with the local stakeholders. To persuade the shepherds about the opportunity of implementing the electric fences, several meetings were organized together with the local stakeholders, Piatra Craiului National Park Administration and the project team. At these meetings, the shepherds were informed about the practical advantages of electric fencing use and about the previous experiences of electric fencing and prevention of large carnivore damages caused to livestock. There was highlighted the importance of regular rotation of night resting places and were presented the sustainable grazing schemes and their role for the alpine meadows ecosystems. During these meetings, we noticed a preliminary negative attitude of locals regarding project activities but after an information period and several meetings, the situation changed significantly. In order to continue these activities, the shepherds should be regularly monitored by the park administration.
For crops and orchards protection located
around
The
forest and game administrators, together with the
The shepherd camps monitoring had the following outputs and conclusions:
- All grazing areas within the park zone were delimitated and mapped (fig. 2);
- All grazing routes passed the forested habitats and were noticed significant grazing activities in the forests around alpine meadows;
- The flock speed was higher in the areas with significant erosion on soil and vegetation. This fact had enhanced the negative role of grazing on soil and vegetation degradation (fig. 3);
- The monitored grazing includes four types of forested habitats and five types of pastures. The grazing activities are not selective in relation with habitat types but the main parts of these activities are carried out on dry pastures and mixed forests habitats. Also, grazing in young mixed forests (regeneration) was found and in some areas this fact had led to significant soil erosion (fig. 4).
- The highest erosion intensity occurs in the forested areas and is correlated with habitat types, steepness and flock speed. The habitats affected by the intensive soil erosion are: pastures of altitude (steepness and flock speed), old coniferous forests, successive wet pastures and clear mixed forests (fig. 5).
The lowest erosion intensity was found on dry pastures, parts of successive wet pastures and parts of clear mixed forests.
- Electric fence use is a new method for protecting Romanian livestock. Therefore, we have observed a reticence of shepherds regarding this method but through an information campaign and direct contacts between project team and them we have gained their active involvement and the effectiveness of these fences led to the fact that 70% of them accepted the use of the mobile fences systems.
- We have some suspicions about the honesty of shepherds when they declared the livestock numbers that are grazing. During monitoring of grazing activities, we have done regular counting on livestock and we have gained accurate information on livestock numbers.
- At the beginning of the electric fencing activities, the project team regularly moved the night resting fences but after few weeks, the shepherds started to move regularly the fences, supervised by a member of the project team. This supervising activity will be continuing by the park administration.
- Sometimes, the shepherds forgot to power on the electric source of fences but through regular monitoring, they get used with the new method and followed the rules for a correct use.
- The shepherds tend to exaggerate when they declare the damages, in order to get more money from hunting units administrators or from insurances companies. This damage evaluation is a problem that has to be solved in the future. ICAS is already initiating several actions that will address this issue and we look forward to find national partners for developing an insurance system that could be used by the majority of Romanian livestock owners. Nowadays the insurance fee is relatively high and is not attractive for the livestock owners. Also, there are no experts for damage evaluation and this is done on a bureaucratic way.
- The electric fencing had immediate results and livestock damages level was significantly decreasing. Thus, in 2001, when the traditional methods were used for livestock protection, the damages were 1.23 % of the total number of livestock. After the prevention methods started to be implemented by the project, the level of damages have significantly decreased: 0.49% in 2002, 0.17% in 2003 and 0.44% in 2004 (fig. 1). Regarding the situation in 2004, we would like to mention that the number of daytime large carnivore attacks was increasing and during daytime the livestock are not protected by the electric fences (on daytime livestock are grazing on itinerary).
Figure 1.
Livestock damages caused by large carnivores from the total livestock number in
Figure 2. Daily sheep flock activities
Figure 3. Sheep flock speed on grazing routes
Figure 4. Grazing routes and habitat types
Figure 5. Erosion and habitat types
There is a need of continuation of these activities in the next years. The ICAS project team will support the national park administration by providing the electric fencing equipment and by training the park staff on issues related to use of the mobile electric fences system and monitoring grazing activities. Based on the future gained data it could be implemented an integrated grazing management system in Piatra Craiului that will use electric fencing for livestock protection, insurance system for damage prevention and sustainable grazing on alpine meadows. In this respect, we consider that is essential to have a close cooperation between all the relevant stakeholders and to use nature conservation as a benefit for local people.
Acknowledgements
We would like to thank for their valuable inputs to: Prof. Dr. Theodor Marusca (Transylvania University Brasov), Anca Ioanitescu (Environmental Protection Agency Brasov), Oliviu Pop (Piatra Craiului National Park), Ovidiu Ionescu (ICAS - Forest Research and Management Institute Brasov), Serban Negus (ICAS - Forest Research and Management Institute Brasov), Ioan Noaghea (AJV Brasov - Hunters Association Brasov) and Gheorghe Iordache (ITRSV Brasov - Inspectorate for Forest and Wildlife Management Brasov).
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SAVELLI, F. ANTONELLI & L. BOITANI, 1998: The Impact of livestock support
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DWYER, D. BALDOCK, G. BEAUFOY, H. BENNETT, P. LOWE & N. WARD, 2002: Rural
Development in an Enlarging European Union, WWF
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***, 2002: Large Carnivore Action Plans for Europe, Council of Europe.
ANIMALELE DOMESTICE SI CARNIVORELE MARI IN
PIATRA CRAIULUI
Lucrarea prezinta diferite tipuri de activitati care urmaresc asigurarea conservarii pe termen lung a populatiilor de carnivore mari in zona Piatra Craiului. Aceste actiuni sunt reprezentate de: lobby si consultarea grupurilor de interese, protectia cu garduri electrice a animalelor care pasuneaza, monitorizarea pradarii cauzate de carnivorele mari, realizarea unor actiuni de constientizare prin tabere de voluntari, informarea opiniei publice. Toate aceste activitati au fost derulate prin utilizarea unei abordari integrate, focalizata pe prevenirea si reducerea posibilelor conflicte dintre ursi, lupi si rasi, pe de o parte si activitatile de crestere a animalelor pe de alta parte. Rezultatele specifice fiecarei activitati au fost integrate intr-un set de concluzii care a fost utilizat la elaborarea liniilor directoare pentru managementul populatiilor de carnivore mari din zona Parcului National Piatra Craiului. Aceste activitati sunt replicate in alte zone din Romania (vezi proiectul LIFE Natura din judetul Vrancea LIFE Nature 02/NAT/RO/008576 - perioada de implementare 2002 - 2005) iar, pe plan local, vor fi continuate de catre administratia Parcului National Piatra Craiului.
Cuvinte cheie carnivore mari, animale domestice, pasunat, garduri electrice, pradare
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