Landscapes Forest and Global Change - ESA - Escola Superior ...

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M. Akbarzadeh & E. Kouhgardi 2010. Mapping and monitoring land cover and land –use changing using RS and GIS 335 Table2. Change detection details of study area Class Name 1987 (area in ha) 2002(area in ha) Crop land Bairsoli H.Forest L.Forest Rangeland River Total area 400.52 21128.71 5089.26 14036.59 9049.88 303.7 50008.66 654.76 21931.34 4086.3 13987.45 9021.29 327.52 50008.66 The next land degradation process cause in the study area is water erosion and wind erosion, which are so power full, in lands without vegetation cover or low vegetation cover. Water and wind erosion let to the removal of the relatively fertile top soil and this could lead to desertification. 4. Discussion The objective of this study was to provide a recent prespective for land cover types and land cover changes that have taken place in the last fourteen years, to integrate visual interpretation with supervised classification using GIS and to examine the capabilities of integrating remote sensing and GIS in studying the spatial distribution of different land cover changes. The area of forest stands has decreased considerably. Integrating GIS and remote sensing provided valuable information on the nature of land cover changes especially on the area and spatial distribution of different land cover changes. The main causes of land degradation in the study area are convertion of forest stands to range lands, range lands to crop lands, and convertion of crop lands to bare lands. This problem show sere to be continued for disclimax and needs to be seriously studied, through References Akbarzadeh, M., 2007. Using RS and GIS for Land evaluation in Arasbaran Iran. Ph.D. thesis, IAU, Science and Research University, Tehran, Iran. Darvish sefat, A., Makhdum, M., and Jafarzadeh, H., 2002. Using GIS and RS in natural resources.Tehran University Press, 250 p. Milne, A., 1988. Change detection analysis using Landsat imagery a review of methodology. Proceedings of IGARSS, 88 symposium, 541–544. Stow, D., 1999. Reducing mis-registration effects for pixel-level analysis of land-cover change. International Journal of Remote Sensing, 20: 2477–2483. Forest Landscapes and Global Change-New Frontiers in Management, Conservation and Restoration. Proceedings of the IUFRO Landscape Ecology Working Group International Conference, September 21-27, 2010, Bragança, Portugal. J.C. Azevedo, M. Feliciano, J. Castro & M.A. Pinto (eds.) 2010, Instituto Politécnico de Bragança, Bragança, Portugal.
B. Baran-Zgłobicka & W. Zgłobicki 2010. Forest patches in agricultural landscapes (loess areas of SE Poland) 336 Forest patches in agricultural landscapes (loess areas of SE Poland) Bogusława Baran-Zgłobicka & Wojciech Zgłobicki Department of Geology and Lithosphere Conservation, Maria Curie - Sklodowska University, Poland Abstract A mosaic of naturally and anthropogenically conditioned patches of terrain cover, which are diversified as regards the kind, size and shape, appears in the agricultural landscapes. The research was carried out in the 2 test areas located in SE Poland. They cover an area of 28 km2 and 35 km2. This is the area of the appearance of a specific landscape in the structure of which, a group of forms characteristic for its loess relief is dominant. The analysis of the changes in the land use were carried out on the basis of the three maps comparison four maps, representing the years 1840, 1890, 1935, 1997. The spatial analysis consisted of the assessment of changes of forest patches areas as well as some chosen statistical parameters prepared for the four time periods: 1840-1890, 1890-1935, 1935-1997, 1890-1997. The studies revealed differences in the scope of changes in the percentage of forest cover in the test areas. Keywords: agricultural landscape, land use changes, loess areas 1. Introduction Agricultural landscapes are characterised by a mosaic of naturally and anthropogenically conditioned patches of land cover that are diverse in kind, size and shape. Human activity is the main factor influencing the changeability of forms of land use in time and space. However, in many cases the influence of abiotic environment components can also be significant. A good understanding of the historical determinants of changes in land usage allows for a better anticipation of the tendencies developing in a landscape, and also enables a more effective landscape management (Bork 1989, Dotterweich 2008). The research was carried out in two test areas, Wąwolnica (28 km 2 ) and Wilczyce (35 km 2 ), located in SE Poland. The structure of the unique landscape occurring in this area is dominated by a group of forms characteristic of loess relief. The deep Bystra and Opatówka river valleys form the morphological axes of the test areas. The plateaus and slopes are dissected by a system of dry valleys and gullies. The Wąwolnica area exhibits a greater diversity of relief as steep slopes and gullies occupy a larger part of the landscape (see Table 1). These areas were cultivated as early as the Neolithic, while the next strong expansion of settlements and farming began in the mediaeval period (Nogaj-Chachaj 2004). Nowadays, arable lands predominate in the land use structure, occupying from 55% to 63% of the whole area. The percentage of forest cover is quite high in the Wawolnica test area (18%), while it is significantly lower in Wilczyce (9%). It is a result of a large proportion of areas where cultivation has been discontinued because most of them are occupied by gullies and steep slopes (Baran-Zgłobicka and Zgłobicki 2004). A typical community growing in gullies and on steep slopes nowadays are Tilio-Carpinetum forests; tree stands are composed of hornbeam (Carpinus betulus) with an admixture of smallleaved lime (Tilia cordata), Norway maple (Acer platanoides) and pedunculate oak (Quercus robur). Protected species occur among herbal plants (Kucharczyk 1992). Forest Landscapes and Global Change-New Frontiers in Management, Conservation and Restoration. Proceedings of the IUFRO Landscape Ecology Working Group International Conference, September 21-27, 2010, Bragança, Portugal. J.C. Azevedo, M. Feliciano, J. Castro & M.A. Pinto (eds.) 2010, Instituto Politécnico de Bragança, Bragança, Portugal.
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Landscapes Forest and Global Change
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The contributions to this volume ha
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Table of contents Foreword Preface
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Fine-scale mapping of High Nature V
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Characterization of a Maculinea alc
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Urban tree inventory and socio-econ
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xiii Foreword Twenty years ago, Dr.
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Section 1 Scaling in landscape anal
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V. Cortes et al. 2010. Environmenta
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D. S. de Ron et al. 2010. Habitat s
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B. Bożętka 2010. Recent relations
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S.F. Chen et al. 2010. A physiotope
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V.D. de Campos & S M. Carvalho 2010
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N.S. Evseeva & Z.N. Kvasnikova 2010
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N.S. Evseeva & Z.N. Kvasnikova 2010
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S. Frank et al. 2010. A regionally
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M. García et al. 2010. The effect
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M. García et al. 2010. The effect
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S. Gholami et al. 2010. Spatial pat
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P. González-Moreno et al. 2010. Th
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T. Höbinger et al. 2010. Impact of
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P. Matos et al. 2010. Can lichen fu
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E.S. Meier et al. 2010. Projections
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E.S. Meier et al. 2010. Projections
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H. Moutahir et al. 2010. Applicatio
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H. Moutahir et al. 2010. Applicatio
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C. Palaghianu 2010. The use of Voro
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F. Peña-Cortés et al. 2010. Spati
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F.M. Rabenilalana et al. 2010. Mult
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A. Ruskule et al. 2010. Patterns of
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E. Sayad 2010. Nitrogen retrancloca
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E. Sayad 2010. Nitrogen retrancloca
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G. Zhelezov 2010. Evaluation of the
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Section 3 Disturbances in changing
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A. Altamirano et al. 2010. Human-ca
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A. Altamirano et al. 2010. Human-ca
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T. Curt & J. Pausas 2010. Are chang
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R.A Fleming et al. 2010. Forest man
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R.A Fleming et al. 2010. Forest man
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P.C. Goebel et al. 2010. How import
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L.R. Iverson et al. 2010. Merger of
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T.-C. Lin et al. 2010. Immediate ef
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K. L. Martin & P.C. Goebel 2010. Im
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G.M. Pastur et al. 2010. Indirect e
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E.W Saragih et al. 2010. Effects of
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L.R.P. Williamson et al. 2010. Anth
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N. Zurbriggen et al. 2010. Modeling
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Section 4 Biodiversity conservation
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Akbarzadeh et al. 2010. Ecotourism
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Akbarzadeh et al. 2010. Ecotourism
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C. Carvalho-Santos 2010. Fine-scale
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I. Catalano et al. 2010. Wood macro
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R.A. Diaz-Varela et al. 2010. Exten
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R.A. Diaz-Varela et al. 2010. Asses
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P.A.E. Diogo & J. Aranha 2010. GIS
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P.A.E. Diogo & J. Aranha 2010. GIS
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V. Etemad & N. Avani 2010. Investig
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A.E. Eycott et al. 2010. The impact
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E. Fernández-Núñez et al. 2010.
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N. Fracassi & D. Somma 2010. Partic
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J. Hartter et al. 2010. Fortresses
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M.B. Horta et al. 2010. Landscape S
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J.O. López-Martínez et al. 2010.
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Sara Marques et al. 2010. Impact of
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M.G.C. Martins & J. Aranha 2010. El
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M.G.C. Martins & J. Aranha 2010. El
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J.-F. Mas et al. 2010. Modeling lan
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R.S. Moro & T.K. Pereira 2010. Eval
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R.S. Moro & C.H Rocha 2010. A metho
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V. Núñez et al. 2010. Landscape i
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V. Núñez et al. 2010. Landscape i
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M. Ortega et al. 2010. Monitoring v
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G. Puddu et al. 2010. Landscape tra
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H.R. Ratsimba et al. 2010. Multi-sc
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M.C. Rodrigues et al. 2010. Charact
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S.M. Scheffer & E. Schimanski 2010.
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A.L. Teixido et al. 2010. Impacts o
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H. Viana & J. Aranha 2010. Assessin
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H. Viana & J. Aranha 2010. Mapping
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Section 6 Tools of landscape assess
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N. Avani et al. 2010. Investigation
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J.C. Azevedo et al. 2010. Spatial d
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T. Batista et al. 2010. The third d
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M. Deconchat et al. 2010. Identific
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J. Gaspar et al. 2010. Visibility a
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J.-F. Mas et al. 2010. Assessing
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A. Matos et al. 2010. Economic valu
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A. Migliozzi et al. 2010. Land-use
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M.L Porto et al. 2010. Naturalness
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M.L Porto et al. 2010. Naturalness
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M. Rehor & V. Ondracek 2010. Applic
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J. Russell et al. 2010. Developing
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Section 7 Management and sustainabi
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P. Angelstam & M. Elbakidze. 2010.
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M. Castro et al. 2010. Relationship
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E. Kouhgardi et al. 2010. Values of
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E. Kouhgardi et al. 2010. Values of
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E. Schimanski 2010. The importance
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L.A.M. da Silva & E. Shimanki 2010.
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N. Stryamets et al. 2010. Role of n
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E. Volkova 2010. The regional analy
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Section 9 Symposia
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Z.L. Urech & J.P. Sorg 2010. Taking
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Measures of landscape structure as
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Network theory to conserve and reco
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B. Terrones et al. 2010. Detecting
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Management and conservation of Medi
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IUFRO Unit 8.01.02 Landscape Ecolog
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