DIGITALNA ARHIVA ŠUMARSKOG LISTA
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ŠUMARSKI LIST 13/2005 str. 28 <-- 28 --> PDF |
S. Matić. I. Anić, M. Oršanić: SILVICULTURAL TREATMENTS AIMED AT IMPROVING THE ANTI-EROSION Šumarski list SUPLEMENT (2005). 17-30 fulfilment, at present and in the future, of fundamental commercial, ecological and social functions at the local and global level without causing harm to other ecosystems. This order is not random. As seen from the list, priority is given to the stability of forest ecosystems and the fulfilment of non-commercial forest functions. Non-commercial forest functions are divided into a) social and b) ecological or protective functions (Prpić 1992). Anti-erosion and water-protective forest functions belong to the latter group. There is extensive scientific literature dealing with this topic in Croatia, especially with relation to biological erosion control and the anti- erosion function of the plant cover: Topic et al (2005), Topic (2001, 1996, 1995), Komlenović et a/(1992), Vidaković et al (1984). According to Prpić (1992), the fulfilment of the anti-erosion function depends on the relief, exposure, soil and precipitation. This author points out that the impact of forests on water protection is determined by site and forest stand. Important factors in this respect include the relief, geological substrate, soil, the type of tree species making up a stand, stand´s age and crown canopy. Hence, the structure of a forest stand is one of the distinctive factors that contribute to the anti-erosion and water-protective forest function. The structure of a forest stand is the result of silvicultural treatments. Silvicultural treatments are aimed at regulating and sustaining the structure of a forest stand in accordance with the silvicultural properties of a tree species forming the stand, site characteristics and management objectives. If the structure of a forest stand is regulated and maintained with silvicultural treatments, then these treatments can also be used to regulate the anti-erosion and water-protective function of a forest stand. There are two main groups of silvicultural treatments: forest tending and forest regeneration. Forest tending influences the forest stand and its site in such a way that it sustains the optimal structural condition that ensures its stability, diversity, productivity and capacity for natural regeneration. This condition should be maintained permanently regardless of whether the stand in question is an even-aged or an uneven-aged forest. The next logical silvicultural step involves the ability of the tended stand to regenerate naturally, which will guarantee sustainability provided the regeneration treatments are applied professionally. No forest management objective is a gift of nature and none can be achieved if a stand is left to natural processes and spontaneous growth. The objectives can only be achieved is a stand is properly tended. Tending regulates the development of a stand in accordance with natural laws and makes optimal use of the site conditions, biological properties and ecological requirements of a species being tended. Forest regeneration is the replacement of one generation of a forest stand with another or the replacement of a mature tree with a young tree. This is the most sensitive and the most complex process in the life of a forest. It is accomplished with the shelterwood method. Care should be taken not to inflict any stresses on forest site. The shelterwood method ensures the replacement of one generation with another at a minimal shock for the forest site and the forest soil in particular. The task of creating a new generation is complemented with that of preserving the forest soil from adverse effects which may cause degradation processes. According to Varal ly ay (1998), these effects include water- and wind-induced soil erosion, acidification, salinization, alkalization, physical degradation (compacting, breaking up the structure and similar), changes in the moisture regime (a drop in the groundwater table, water logging, drying), biological degradation (reduced range of species and their biological activity), unwanted changes in the bio-geo-chemical and nutritive cycle, contamination of soil with toxic substances, lessened adsorption capacity, and soil coverage with ground weed vegetation, invasive tree species (false acacia) and shrubs (false indigo). This article explores some specific features of silvicultural tending and regeneration which are used to improve the anti-erosion and water-protection forest function. We will particularly focus on several historical silvicultural methods in Croatia. Some examples of pedunculate oak forests, selection forests and forests in the Mediterranean region of Croatia will be analysed. FORESTS OF PEDUNCULATE OAK Tending forest stands was introduced in the Croatian forestry practice at a very early date. Tending treatments performed according to particular developmental stages were done simultaneously with the regeneration of virgin stands and the growth of the first generation of commercial forest stands. In Croatia, the first written sources on forest tending, and in particular on the tending of pedunculate oak, date from the end of the 19th century, shortly after the first articles in the field of forest regeneration were published. As early as 1878, Pauz i n published an article on thinning in young stands. H an k o n y i (1890) discusses the tending of oak forests with cleaning, i.e. the removal of shrubs, poplars, willows and other species. Kozarac (1897) describes the tending of young oak stands in the seedling and young growth developmental stages. He |