Abstract:This paper studies the assessment of sensitivity to land degradation of Deliblato sands (the northern part of Serbia), as a special nature reserve. Sandy soils of Deliblato sands are highly sensitive to degradation (given their fragility), while the system of land use is regulated according to the law, consisting of three zones under protection. Based on the MEDALUS approach and the characteristics of the study area, four main factors were considered for evaluation: soil, climate, vegetation and management. Se… Show more
“…The main historic periods of deforestation occurred in the last millennium and, more pronounced, in the Middle Ages (Darby, 1956;Kaplan, Krumhardt, & Zimmermann, 2009). In some places in Europe, however, some traces of the former deforestation have been preserved in the form of drift sands and migrating dunes (Kadović et al, 2016;Koster, 2009;Petrić, 2009). In many cases, these small anthropogenic 'deserts' have existed in the landscape for at least 200-300 years, resulting in unique features.…”
Section: Introductionmentioning
confidence: 99%
“…For decades, drift sands were treated as wastelands, and when the damage associated with its existence, such as burying roads, ditches, houses, and arable fields became onerous, drift sands were afforested (Castel II, Koster, & Slotboom, 1989). In this way, for example, the coastal dunes on the Curonian Spit, Lithuania/Russia (Povilanskas, Baghdasarian, Arakelyan, Satkūnas, & Taminskas, 2009), migrating dunes in Denmark (Christensen & Johnsen, 2001), inland dunes and drift sands in Serbia (Kadović et al, 2016), Croatia (Petrić, 2009), or in the Netherlands (Riksen et al, 2006) were partly afforested.…”
The Silesian‐Cracow Upland, due to the exceptionally large reserves of various natural resources, was under the influence of intense human activity throughout the last millennium. Economic development of the Upland began in the Middle Ages by mining and smelting of iron ore, silver, and lead; from the 18th to the 20th century, the area experienced intense exploitation of coal, zinc and lead ores, stowing sands, as well as dolomites and limestone. Mining and metallurgy have almost always been associated with deforestation. The sandy substrate devoid of vegetation was subjected to aeolian processes, resulting in numerous fields of drift sands. In this paper, based on the analysis of archival and contemporary cartographic materials, as well as historical and archaeological studies and field research, spatial distribution of drift sands was determined, its origin, the time of creation, and durability in the landscape. Research showed that drift sands appeared in the Middle Ages and its ‘desert’ character persisted for 200–300 years, often even for 400–500 years. In the second half of the 20th century, most of the former areas with drift sands were afforested. Currently, bare sands are found only on 2 areas in the Silesian‐Cracow Upland. As unique landscapes, they require special protection because of the biodiversity and geodiversity. Research confirmed that historical interpretations are a valuable source of information about the old landscapes. This knowledge can and should be used by local authorities, institutions, and societies to manage the space, respecting the traces of the settlement and the economic past.
“…The main historic periods of deforestation occurred in the last millennium and, more pronounced, in the Middle Ages (Darby, 1956;Kaplan, Krumhardt, & Zimmermann, 2009). In some places in Europe, however, some traces of the former deforestation have been preserved in the form of drift sands and migrating dunes (Kadović et al, 2016;Koster, 2009;Petrić, 2009). In many cases, these small anthropogenic 'deserts' have existed in the landscape for at least 200-300 years, resulting in unique features.…”
Section: Introductionmentioning
confidence: 99%
“…For decades, drift sands were treated as wastelands, and when the damage associated with its existence, such as burying roads, ditches, houses, and arable fields became onerous, drift sands were afforested (Castel II, Koster, & Slotboom, 1989). In this way, for example, the coastal dunes on the Curonian Spit, Lithuania/Russia (Povilanskas, Baghdasarian, Arakelyan, Satkūnas, & Taminskas, 2009), migrating dunes in Denmark (Christensen & Johnsen, 2001), inland dunes and drift sands in Serbia (Kadović et al, 2016), Croatia (Petrić, 2009), or in the Netherlands (Riksen et al, 2006) were partly afforested.…”
The Silesian‐Cracow Upland, due to the exceptionally large reserves of various natural resources, was under the influence of intense human activity throughout the last millennium. Economic development of the Upland began in the Middle Ages by mining and smelting of iron ore, silver, and lead; from the 18th to the 20th century, the area experienced intense exploitation of coal, zinc and lead ores, stowing sands, as well as dolomites and limestone. Mining and metallurgy have almost always been associated with deforestation. The sandy substrate devoid of vegetation was subjected to aeolian processes, resulting in numerous fields of drift sands. In this paper, based on the analysis of archival and contemporary cartographic materials, as well as historical and archaeological studies and field research, spatial distribution of drift sands was determined, its origin, the time of creation, and durability in the landscape. Research showed that drift sands appeared in the Middle Ages and its ‘desert’ character persisted for 200–300 years, often even for 400–500 years. In the second half of the 20th century, most of the former areas with drift sands were afforested. Currently, bare sands are found only on 2 areas in the Silesian‐Cracow Upland. As unique landscapes, they require special protection because of the biodiversity and geodiversity. Research confirmed that historical interpretations are a valuable source of information about the old landscapes. This knowledge can and should be used by local authorities, institutions, and societies to manage the space, respecting the traces of the settlement and the economic past.
“…Saadoud et al [32] and Mezösi et al [33] further investigated air temperature and precipitation. In a particular area of AP Vojvodina (Deliblato sands), Kadović et al [34] pointed to the drought factor in relation to the soil degradation caused by desertification processes. In a study carried out in AP Vojvodina, Savić et al [35] investigated the climate factor using the de Martonne aridity index [36], along with wind velocity data.…”
Wind erosion is one of the most significant forms of land degradation which occurs in arid and semi-arid regions. Agricultural land is significantly affected by wind erosion, which leads to soil quality reduction, and consequently to economic losses. This research was conducted in the autonomous province (AP) of Vojvodina (a region dominated by agriculture), which represents one of the most important economic regions in the Republic of Serbia. The aim of this research was to identify areas sensitive to wind erosion (in the month of March) in the AP Vojvodina by using fuzzy logic, remote sensing data, and geographical information systems (GIS). The data of prior research on erosion sediment were used for results validation. The results show that the hazardous sensitivity category covers approximately 60.41% of the research area, while the medium sensitive category accounts for 36% of the area. These findings are primarily a result of the lack of vegetation in almost the entire area, particularly in wind-exposed agricultural areas with no vegetation, which are being prepared for sowing. Another factor putting such a large area at risk is the unfavorable climate (especially in southeastern parts of the area), and slightly less favorable soil properties in the north. The results of this research could be used in decision-making at the regional level, along with the development and implementation of programs aimed at mitigating the effects of wind erosion.
“…The textural sand class belongs to highly erodable soils, loamy sand with medium erodable soil, while sandy clay belongs to poorly erodable soil (Кадовић и сар., 2014). In addition to the aforementioned factors, eolic erosion process in the territory of the Deliblatska sands is a result of characteristic pedological features (moisture content, chemistry, content of organic components), climatic characteristics, vegetation cover and the influence of anthropogenic factor (Kadović et al, 2016).…”
Section: The Influence Of Forest Vegetation On the Stabilization Of Ementioning
The paper analyzed basic physical-geographical characteristics and changes caused by afforestation. The aim of the paper is to point out the transformation of the natural environment initiated by afforestation, to present positive and negative implications of this action, and to emphasize the importance of the consideration of the cause-and-effect relationships during concrete action in the field. By applying analytical-synthesis and comparative methods, a presentation of the natural features of the Deliblato sand and changes that were made as a result of afforestation, is given. The results of the research present positive changes which are reflected in the stabilization of unbound sand, development of the pedogenetic process and improvement in the microclimate conditions in the forested sectors. Negative changes in afforestation are reflected in the reduction of the area's steppe vegetation and the consequent intensity of forest fires.
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