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ŠUMARSKI LIST 1-2/2017 str. 56     <-- 56 -->        PDF

their roles in the ecosystem process (Samman and Logan 2000), it is a requirement to suppress their outbreak populations. The purpose of control programs planned against these species is to effectively reduce their damage levels in the stands (Faccoli and Stergulc, 2008). Removing weak and damaged trees found in the area before the population density of I. sexdentatus, which is a pest, reaches to a level that will attack healthy trees, including trees that are slightly injured or healing, will decrease the dying risk of healthy trees (Fernández Fernández, 2006). Bark beetle invasions start in damaged and/or stressed trees (Douce, 1998). Long term disturbances causing stress in tree may lower the resistance of trees, and therefore trees may become sensitive even in low beetle densities (Power et al., 1999). Stressed trees are more sensitive to I. sexdentatus attacks. For this reason, in forest areas where fire or wind weakened trees are present, beetle attacks may be more (Seedre, 2005).
In light of the explanations, in a healthy ecosystem where natural balance is preserved; utilizing our forests through sustainable planning is one of the main principles of today’s forestry. In these planning, bark beetles, one of the factors that has the potential to cause high damage, causing unplanned cutting in cases of outbreaks and therefore threatening our forests, is important in terms of forestry. In the black pine forests, which has important propagation through stands they form in Turkey, explaining the flight periods, capturing rates and some factors affecting the capturing of I. sexdentatus and understanding the damage the species may cause in endemic levels will contribute to increasing effectiveness of control programs to be carried out.
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