Transactions on Ecology and the Environment vol 60, © 2003 WIT Press, www.witpress.com, ISSN 1743-3541 Estimation of the torrential environment (potential) of isle Zakynthos (Greece) using GIS P. stefanidisl & I. ~alinderis' I Institute of Mountainous Water Management and Control, Aristotle University of Thessaloniki, Greece. Abstract The torrential conditions of an area are determined by four basic factors: Climate, geologic support, relief and vegetation. The combination of the factors, mentioned above, in a particular basin or in a wider area, brings about an energy system, called "torrent potential". The climate is a factor attacking the geological support, while the vegetation, wherever it exists, acts as a protective cover. The relief has a regulative effect: precipitous of flat relief aggravates or moderates accordingly the torrential phenomena. Therefore the torrent potentials of an area determine the process and the way the overland flow, moves. Mediterranean climate demonstrates certain particularities, with the long-drawnout dry and hot period during summer but also the intense rainfalls during autumn and winter. These particularities cause respectively severe problems of draughts and floods. In this paper study, the torrential environment (potential) of isle Zakynthos in Greece is determined. Initially the area was mapped (scale 1:50000). The torrent basins were delimited and the basic factors (Climate, geologic support, relief and vegetation) were estimated using G.I.S. Finally, the torrential environment (potential) was determined and the proper watershed management system was suggested in order to prevent the problems of water deficiency and of flooding. Transactions on Ecology and the Environment vol 60, © 2003 WIT Press, www.witpress.com, ISSN 1743-3541 120 River Ba~itlMarragernctlr I1 1 Introduction Greece is a mountainous land, whch receives a great amount of intense rainfall. Its geologic support consists of rather highly erodible rocks. That fact in combination with the lack of plant cover, which is a highly protective factor against erosion, and also with the immense man-made interference, causes the development of many disastrous torrents on Greek land. Torrents introduce a certain characteristic, which is described by the removal, the transport and the deposit of debris from highlands to lowlands. As a result the torrent basins on highlands are being degraded while on the lowlands debris causes serious problems by alluviating streambeds and lakes. The torrential conditions of an area are determined by four main torrent factors: Climate, geologic support, relief and vegetation. The combination of those factors in a particular basin or in a wider area brings about an energy system, called "torrent potential". It's the torrent potential, which appoints the way of the outflow of the torrents (Kotoulas, 1972). The climate is a factor attacking the geologic support, while vegetation wherever it exists, acts as a protective cover. Relief has a regulative effect: precipitous or flat relief aggravates or moderates accordingly the torrential phenomena. The rational confrontation of the intense torrential problems in Greece necessitate the research of torrent conditions and the classification of torrents in certain types. Therefore the proper watershed management system must be determined. The multiprocessor system that G.I.S. offer combined with the ability of processing spatial data and attributes, makes their use irreplaceable. In this paper study, the torrential environment (potential) of isle Zakynthos in Greece is determined, with the use of G.I.S. 2 Bibliography review Many researchers have tried to classify mountainous basins of torrents. In 1826 Duile was the fist who attempted to classify mountainous watersheds. Since then, the most important researches were made by, Sure11 [10], Demonzey [3], Stiny [9], Margaropoulos [8], Kotoulas (1972). The classification Kotoulas introduced, was the only classification, which defined specific torrent types. Besides those, there is also Aulitzky's [l] classification of depositional formations and debris cones, which relates mainly to the hazardous activity of torrents in Austria. The main features of Kotoulas [5] classification, which was used also in the specific paper, are the following. Three out of four basic torrent factors (Relief, Climate and Vegetation) are depended on the maximum elevation (Maximum torrential elevation). The sea water level, the limit of the full forest cover impact, the natural forest cover limit as well as the limit of everlasting snow determine the torrent environment in which watersheds are developed (Fig. 1). 1. Torrent environment I. 0 - 1 0 0 0 ~ Transactions on Ecology and the Environment vol 60, © 2003 WIT Press, www.witpress.com, ISSN 1743-3541 2. 3. Torrent environment 11. l OOlm - 2 0 0 0 ~ Torrent environment 111. 2001 - 3000m (Alpine zone) Torrent environment IV. > 3001m Zone of everlasting snow 4. In Greece only the first three torrent environments are formed. As far as the geologic support is concerned, in order to associate torrential phenomena to predominating rocks in each basin, rocks were classified in torrential petrographical formations according to their liability on extreme weather conditions. The results of this classification are the following: M = Crystalline, igneous or magmatic rocks S = Sedimentary rocks G = Schist (slate) rocks K = limestone rocks F = Flysch rocks Basins composed by only one torrential petrographical formation, or composed by more than one, but their percentage is lower than 15%, are described as unmixed, while others are described as mixed ones. A basin described as an M I type, means that it's an unmixed watershed, which its geologic support consists of crystalline rocks, and belongs to torrent environment I (0 - 1000m). A basin described as an M,G - I1 type, means that it's a mixed watershed, which its geologic support consists of crystalline rocks and Schist (slate) rocks, and belongs to torrent environment I1 (1001 - 2000m). - Torrent Enxuvnment I1 Toruent Enrilvnment I Figure 1: Torrent environments according to the Kotoulas [5] classification 3 Research area Our research was conducted in Zakynthos island in Ionian Sea (Fig. 2). It is one of the rainiest areas in Greece. Zakynthos has an extent of 406.0. Kid and its population exceed 39.015 people. During summer it attracts a great number of tourists. Transactions on Ecology and the Environment vol 60, © 2003 WIT Press, www.witpress.com, ISSN 1743-3541 122 River Ba~itlMarragernctlr I1 4 Research method For the accomplishment of the goals of this research, the following methods were applied. The research area was mapped (scale 1:50000). The watersheds were defined and the whole area was digitised. The contours were also digitised (contour interval 100m). The watersheds were counted and encoded. Using Arc/Info 3.5.1 for pc and ArcIView 3.2, the morphological features were determined. The total area drainage basin (F), Perimeter (U), degree of Hmed),maximum relief (H,) and basin's mean roundness (B), altitude (H-, H,, slope (J). After that the basic torrent factors were analysed and the torrent potential of each torrent was defined. In order to complete the above mentioned research The meteorological dates of the existing weather stations were collected, interpreted and revises A vegetation (plant cover) map was conducted (scale 1:50000), using satellite data, thematic maps and aerial photographs The kinds and the extension of the torrential petrographical formations in the research area were defined, based on the geologic maps of Greece (scale 1:50000), which were digitized and processed by G.I.S. The contour lines were digitized and processed by G.I.S. On completion of the above-mentioned work and after the determination of the torrent environment, torrents were classified in torrential types. 5 Results 5.1 Torrent basins, morphological features It is generally known that the most important morphological features that affect torrent attributes are the total basin area (F), the perimeter (U) the degree of roundness (B), elevation (Hfin, H-, Hmed),Maximum Relief (H,) and basin's mean slope (J). These morphological features were estimated and used in our research. Table 1 lists the values of the morphological features described for every torrent basin in Zakynthos. Figure 2 shows the research area, the total drainage system and the watersheds. 78 watersheds drain Zakynthos. The total basin area varies from 0.27 ~ m (No ' 5) to 29.40 ICrn2 (No 26). According to the elevation of < Zakynthos, all 78 torrents are classified in Torrent environment I (H, l OOOm). The basin's mean slopes vary from 11.69% to 55.24%. Transactions on Ecology and the Environment vol 60, © 2003 WIT Press, www.witpress.com, ISSN 1743-3541 Transactions on Ecology and the Environment vol 60, © 2003 WIT Press, www.witpress.com, ISSN 1743-3541 124 River Ba~itlMarragernctlr I1 5.2 Relief In Figure 3 is shown the distribution of contours in Zakynthos Island. It's clearly evident that 35% of Zakynthos area is under 1OOm altitude and 65% varies Erom 0 - 700m altitude. Moreover, torrent's relief range from fair to harsh, a fact that acts in favor of the emergence of extreme torrential phenomena such as floods. 5.3 Vegetation - plant cover Vegetation (plant cover) and especially forest cover is the torrent basic factor that prevents torrent action. In order to define the types of vegetation in Zakynthos, the following method was used. Information on plant cover was extracted from Corine - Landcover, a European project that defines vegetation using satellite data (Landsat - MMS, pixel resolution 25m), thematic maps (scale 1:100000) and aerial photographs. In table 2 is shown the different types of land use that exists in Zakynthos. In figure 5 is presented the map with the different types of land use. Table 2: Land use in Zakynthos island Types of Vegetation Forests Agricultural areas Evermeen broadleaved species Partially forested area Grazing land Area (~rn') 9.1 1 97.32 100.20 33.69 26.33 % 3.39 36.26 37.33 12.55 9.81 According to table 2, forests whose existence prevents torrential phenomena occupy only 3.39%. 5.4 Geologic support In figure 6 is presented the area distribution of rock formations in Zakynthos Island. According to our research, Zakynthos island consists mostly of limestone rocks (74.42%, see Table 3). The rest of the area consists of sedimentary rocks (25.59%). Both these rock formations act in favour of the emergence of torrential phenomena and especially in the production of sediment loads. Table 3: Torrential petrographic formations in Zakynthos island - Torrential Petrographic Formations Limestone rocks (K) Sedimentary rocks (S) Area ( ~ m ' ) 199.81 68.72 % 74.41 25.59 Transactions on Ecology and the Environment vol 60, © 2003 WIT Press, www.witpress.com, ISSN 1743-3541 5.5 Climate Islands in Ionian Sea accept a great amount of rainfalls (Mean yearly height of rainfall 995.31-1114. The distribution of rainfall throughout the year is not normal. During autumn and winter intense rainfalls cause severe problems, while in summer rainfalls are minimized. Table 4: Mean annual rainfall in Zakynthos island Months Rainfall (mm) Months Rainfall (mm) J 162.8 J F 114.5 A 4.2 8.3 M 86.2 S 39.1 A 44.0 0 131.5 M 18.8 N 153.0 J 11.4 D 221.5 Annual 995.3 It is important that in addition to the abnormal distribution of rainfall, intense maximum daily rainfall depth aggravates the torrential phenomena (Maximum daily rainfall depth: 182.0 d 2 4 h ) . 5.6 Torrential environment, torrential types The main factor that has a strong impact on the kind of torrential phenomena that will occur is the geologic support of the watershed (Kotoulas, 1972). Based on that fact and after a spot test, an effort was made in order to classify the different torrential environments, found in Zakynthos island, in specific torrential types. In order to accomplish this, the Kotoulas method, mentioned earlier, was used. According to our research, 51 watersheds are classified in K - I type, 20 watersheds are classified in S I type and just 7 watersheds are classified in the mixed K,S - I type. The torrential phenomena that torrential types produce are given below. Unmixed type K - I Torrential environment: Rock Formation: Limestone (Limestones, dolornites, hornstone, marbles or crystalline limestones) Elevation 0 - 1000m. Torrent phenomena: Intensive sheet erosions, weatherings, gully erosions and landslides. Unmixed type S - I Torrential environment: Rock formation: Sedimentary (sands, clay, conglomerate, breccius, sandstones, mollasic sediments) Elevation 0 - l OOOm Torrent phenomena: Intensive sheet and rill erosions, gully erosions, landslides, lateral erosions. The mixed type K,S I produces torrential phenomena similar to those produced by the unmixed ones, depending on the extent of the petrographic formations. - - Transactions on Ecology and the Environment vol 60, © 2003 WIT Press, www.witpress.com, ISSN 1743-3541 126 River Ba~itlMarragernctlr I1 Figure 2: The Drainage network system of Zakynthos island 6 Torrent control - watersheds management system The outcome of our research showed that the features that best describe torrents of Zakynthos Island are the following. Torrents belong to the hilly, semi mountainous areas with an extent of 0 . 2 7 ~ mto~ 29.40 Km2. The torrential environment is such that produces moderate as well as intense torrential phenomena. The limited forested area as well as the intense human interference in the streambeds of torrents result in the occurrence of many floods. The extreme torrential phenomena that appear in Zakynthos island necessitate the application of Forestry techniques and torrent control works system. The application of the system will lead to the prevention of the existing problems as well as in the enrichment of underground water. Moreover the utilization of planting techniques in combination with technical works will stabilize soil and will help in the untroubled abduction of water. Transactions on Ecology and the Environment vol 60, © 2003 WIT Press, www.witpress.com, ISSN 1743-3541 Figure 3: Relief of Zakynthos island (contour interval 100m) Figure 4: Land use in Zakynthos island Transactions on Ecology and the Environment vol 60, © 2003 WIT Press, www.witpress.com, ISSN 1743-3541 128 River Ba~itlMarragernctlr I1 Figure 5: Area distribution in Petrographic Formations I I Figure 6: Area distribution in torrential types Transactions on Ecology and the Environment vol 60, © 2003 WIT Press, www.witpress.com, ISSN 1743-3541 7 Conclusions - results In our study the torrential environment and torrential types in Zakynthos island were determined and described, using G.I.S. The research was based on bibliography available on torrential environments, torrential types. All the data collected concerning the four basic torrential factors (Relief, climate, geologic support and vegetation) were processed by G.I.S. The results derived by this procession lead us to the determination of the torrential types that exist in Zakynthos island. The knowledge of torrential types helps in the determination of the appropriate management system that should be applied. G.I.S. offer great help in the procession of spatial variation of torrential factors and is a great tool in the research of mountainous water management systems. References [ l ] Aulitzky H., Preliminary two - fold classification of torrents. Mittelungen der forstlichen bundewersuchanstalt, Wien, p 144, 1982. [2] Chow V. T., Handbook of applied Hydrology, USA 1964. [ 3 ] Demonzey P,, L ' extension des torrents en France par le reboisement. Paris, 1878. [4] Jones C, Geographical Information Systems and computer cartography. Logman Scientific and Technical, London 1998. [5] Kotoulas D., Die Wildbache Suddeutschlands und Griechenlands, Teil 1. Bericht Nr. 25. Munchen, 1972. [6] Kotoulas D., Die Wildbache Suddeutschlands und Griechenlands, Teil 2. Bericht Nr. 3 1. Munchen, 1972 [7] Magure J, David and al, Geographical Information Systems principles and applications. (Logrnan Scientific and Technical), USA 1991 [S] Margaropoulos P., Rapport sur la classification des bassins torrentiels FAO/EFC/TORlU64/2, 1964. [9] Stiny J., Die geologischen Grundlagen der verbauund der Geschiebeherde, Wien 1931. [l 01 Surell, Etude sur les torrents des Hautes - Alpes, Paris, 1842. Transactions on Ecology and the Environment vol 60, © 2003 WIT Press, www.witpress.com, ISSN 1743-3541 130 River B a i t 1 M a r r a g e r n ~ t ~I!r
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