У представленій статті висвітлено результати оцінки ландшафтної репрезентативності об"єктів природно-заповідного фонду території Лівобережної України, які являють собою необхідний базис пошуку шляхів оптимізації мережі ПЗФ та екомережі у відповідності до положень концепції ландшафтного різноманіття, засобами ландшафтного планування.
Nowadays landscape planning understood as a special direction of landscapeology which actively develop and has so many linkages with environment optimization and such territory ordering which has a high concordance with a landscape-ecological priority specified by the nation. In accordance with them, nature-conservative function became top-priority for implementation in any region. The theoretic-methodological contemporary apparatus of the nature reserved fund (NRF) exploration formed by scientific results which we could find out in works of European and Ukrainian scientists, in particular: M. Grodzinskyi, P. Shyschenko, V. Paschenko, S. Kukurudza, etc., and international and national standard acts. Nevertheless, lack of works which could clarify questions of landscape representativeness of nature reserved fund objects under conditions of considerable fragmented and anthropogenic territories leads us to accomplishmen&t becoming exploration.
Thus, the aim of the article is to determine landscape representativeness (at the levels of type, genius and sort of landscape complexes) of nature reserved objects by using results of our mapping modelling of landscape-typol&ogical structure of the Left-Bank the Dnipro river of Ukraine territory and the nature reserved fund, which could be a good background for choosing criteria of landscape planning typological units distinguishing and for the future possibility of usag&e it for the purpose of landscape planning tools implementation.
The region of the exploration - the Left-Bank the Dnipro river of Ukraine territory - is understood as a totality of four administration region of Ukraine, such as Poltavsjka, Sumsjka,& Harkivsjka, and Chernighivsjka. The levels of landscape representativeness were determined by using GIS-parcel MapInfo Professional 10.0.1, and type, genius, and sort of landscape complexes data, including 1 552 objects of nature reserved fund (by 1&.11.2016). The methodical basis formed the system of methods such as mapping, graphical, statistic, analysis, and synthesis, etc., especially the method of laying on to each other the mapping models of sort of landscape and the nature reserve fund of& the Left-Bank the Dnipro river of Ukraine territory done by the author. The level of landscape representativeness by the NRF objects is understood as plurality it on the unit of an area according to the next dependence: [формула] where is RLLU - rep&resentativeness of sort or type of landscape by the objects of NRF; nvl - plurality the objects of NRF territory in the definite sort or type of landscape; Svl- square of sort or type of landscape; 100 - probability sum of constituent part/elements o&f the territorial division.
Thus, according to the received results of region landscape representativeness calculation, we summarized that the system of NRF objects has a low level of functional structuring, spatial irregularity, and disproportion d&ue to the landscape representativeness at the level of type, genus, and sort of landscape.
В данной статье представлено результаты оценки ландшафтной репрезентативности объектов природно-заповедного фонда территории Левобережной Украины, которые явл&яют собой необходимый базис поиска путей оптимизации сети ПЗФ и экосети в соответствии с положениями концепции ландшафтного разнообразия, средствами ландшафтного планирования.
