<?xml version="1.0" encoding="UTF-8"?><xml><records><record><source-app name="Biblio" version="7.x">Drupal-Biblio</source-app><ref-type>17</ref-type><contributors><authors><author><style face="normal" font="default" size="100%">Almeida, Mara</style></author><author><style face="normal" font="default" size="100%">Guerra, Carlos</style></author><author><style face="normal" font="default" size="100%">Pinto-Correia, Teresa</style></author></authors></contributors><titles><title><style face="normal" font="default" size="100%">Unfolding relations between land cover and farm management: high nature value assessment in complex silvo-pastoral systems</style></title><secondary-title><style face="normal" font="default" size="100%">GEOGRAFISK TIDSSKRIFT-DANISH JOURNAL OF GEOGRAPHY</style></secondary-title></titles><keywords><keyword><style  face="normal" font="default" size="100%">high nature value</style></keyword><keyword><style  face="normal" font="default" size="100%">land management</style></keyword><keyword><style  face="normal" font="default" size="100%">silvo-pastoral system</style></keyword><keyword><style  face="normal" font="default" size="100%">vegetation cover</style></keyword></keywords><dates><year><style  face="normal" font="default" size="100%">2013</style></year><pub-dates><date><style  face="normal" font="default" size="100%">2013///</style></date></pub-dates></dates><volume><style face="normal" font="default" size="100%">113</style></volume><pages><style face="normal" font="default" size="100%">97 - 108</style></pages><language><style face="normal" font="default" size="100%">eng</style></language><abstract><style face="normal" font="default" size="100%">The high nature value (HNV) concept, proposed by the European Environment Agency, recognizes that specific farming systems support high biodiversity levels, mainly as a result of extensive management practices. The Portuguese montado is one of the most significant HNV systems in southern Europe. However, considering the great complexity characterizing these systems both in land management and in landscape structure, a specific context-oriented methodology to assess which montado areas are likely to be classified as HNV farmland is needed. In this sense, the aim of this study is to explore a methodological approach which makes it possible to assess land management pressures through land cover information on these complex silvo-pastoral systems. The proposed methodology was tested through a local case study in a montado area in southern Portugal, assessing the relation between management practices and a vegetation cover index. Results show that in similar montado areas different land management strategies varying in stocking density, but also in type of grazing animals and shrub control practices, configure different vegetation cycles. These results indicate there is a way to develop a straightforward methodology to assess the HNV value of Mediterranean silvo-pastoral systems based on land cover indicators. These would make it possible to assess the HNV of montado areas with direct and objective information and independent of farmer's surveys or other farm-based data.</style></abstract><issue><style face="normal" font="default" size="100%">2</style></issue><notes><style face="normal" font="default" size="100%">The following values have no corresponding Zotero field:&lt;br/&gt;pub-location: OSTER VOLDGADE 10, COPENHAGEN K, DK 1350, DENMARK&lt;br/&gt;publisher: ROYAL DANISH GEOGRAPHICAL SOC</style></notes></record><record><source-app name="Biblio" version="7.x">Drupal-Biblio</source-app><ref-type>7</ref-type><contributors><authors><author><style face="normal" font="default" size="100%">Kapur, S</style></author><author><style face="normal" font="default" size="100%">Akça, E</style></author><author><style face="normal" font="default" size="100%">Kapur, B</style></author><author><style face="normal" font="default" size="100%">Öztürk, A</style></author></authors><secondary-authors><author><style face="normal" font="default" size="100%">Kepner, W G</style></author><author><style face="normal" font="default" size="100%">Rubio, Jose L</style></author><author><style face="normal" font="default" size="100%">Mouat, David A</style></author><author><style face="normal" font="default" size="100%">Pedrazzini, F</style></author></secondary-authors></contributors><titles><title><style face="normal" font="default" size="100%">MIGRATION : AN IRREVERSIBLE IMPACT OF LAND DEGRADATION IN TURKEY</style></title><secondary-title><style face="normal" font="default" size="100%">Desertification in the Mediterranean Region a Security Issue</style></secondary-title></titles><keywords><keyword><style  face="normal" font="default" size="100%">Land degradation</style></keyword><keyword><style  face="normal" font="default" size="100%">land management</style></keyword><keyword><style  face="normal" font="default" size="100%">Migration (voyant)</style></keyword><keyword><style  face="normal" font="default" size="100%">Soil sealing</style></keyword><keyword><style  face="normal" font="default" size="100%">Turkey</style></keyword></keywords><dates><year><style  face="normal" font="default" size="100%">2006</style></year></dates><publisher><style face="normal" font="default" size="100%">Springer Netherlands</style></publisher><pages><style face="normal" font="default" size="100%">291-301</style></pages><language><style face="normal" font="default" size="100%">eng</style></language><abstract><style face="normal" font="default" size="100%">The total arable land in Turkey is 28.054.000 ha. However, the prime soils cover only 17.5% of the total land surface and the productivity of the remaining soils is mainly limited by topography, depleted organic matter and high clay contents. The long standing deforestation, unsuitable tillage and irrigation management have induced the rate of erosion since historical periods. The majority of the country’s soil (76.5%) are prone to erosion risk due to the dominant steep slopes (&gt;6%), and 72% of the soils are more or less affected from water and wind erosion (CCD-Turkey, 2003). Soil sealing and extraction of raw material together with overuse of fertilizers and irrigation have led to the improper use of traditional environmental friendly agroscape (agroecosystem), thus constantly degrading the soils of the country. Secondary salinity builds up in the primary saline zones as well as the fertile alluvial planes of Turkey, which are actually the gene zones of many crops particularly cereals, legumes and halophytes, pointing out to the reality that irrigation management plans should not only be based on the concept of conventional cash crop production but also for the crop present on the indigenous agroescapes. This necessitates the incorporation of the halophyte production in the central Anatolian steppes and the olive/carod/vine production in the semi-arid Mediterranean karstic region together with the south east Anatolians calcrete agroscapes. This paradigm is sustainable land use management aims to increase the welfare of the urban people and decrease the threat of excess water use in fragile steppe, karstic and calcrete topographies, which are also the carbon pools of the world. Hence, the concept of agroscapes based on landuse assessment should primarily be considered in the development of sustainable land management strategies particularly with the incorporation of indigenous environmental friendly technical knowledge to combat land degradation and desertification. The high population increase in the urban regions and conversely the decrease in the rural, cause the intensive use of arable land around the former inducing desertification. According to the census of 2000, 40%of the country’s population live in rural area (23.797.653 out of the total 67.803.927) with an average of 1.21 ha/man arable land, mostly allocated for cereal production (country average ~2000Kg/ha.). This is equivalent to a low net income rate, which results to migration from the rural areas to urban, particularly from the east of the country to the west. The Government Statistics Institute (2003)date reveals that from 1990 to 2000, the urban population increased by 30%, ie from 33.656.275 to 44.006.274, whereas the rural increased at much lower rate (4.3%). This data reveals the pressure of both natural and human induced factors on soils and land urgently in need of sustainable land management policies along the legislations, since, the rate of quality loss of land and soil, ie desertification in the coming decades will ultimately be the common jeopardy in the country.</style></abstract></record><record><source-app name="Biblio" version="7.x">Drupal-Biblio</source-app><ref-type>7</ref-type><contributors><authors><author><style face="normal" font="default" size="100%">Kosmas, C</style></author><author><style face="normal" font="default" size="100%">Tsara, M</style></author><author><style face="normal" font="default" size="100%">Moustakas, N</style></author><author><style face="normal" font="default" size="100%">Kosma, D</style></author><author><style face="normal" font="default" size="100%">Yassoglou, N</style></author></authors><secondary-authors><author><style face="normal" font="default" size="100%">Kepner, W G</style></author><author><style face="normal" font="default" size="100%">Rubio, Jose L</style></author><author><style face="normal" font="default" size="100%">Mouat, David A</style></author><author><style face="normal" font="default" size="100%">Pedrazzini, F</style></author></secondary-authors></contributors><titles><title><style face="normal" font="default" size="100%">PART . VI Desertification Indicators and Forecasting Techniques ENVIRONMENTALLY SENSITIVE AREAS AND INDICATORS OF DESERTIFICATION</style></title><secondary-title><style face="normal" font="default" size="100%">Desertification in the Mediterranean Region a Security Issue</style></secondary-title></titles><keywords><keyword><style  face="normal" font="default" size="100%">desertification indicators</style></keyword><keyword><style  face="normal" font="default" size="100%">land management</style></keyword><keyword><style  face="normal" font="default" size="100%">land use type</style></keyword><keyword><style  face="normal" font="default" size="100%">soil erosion</style></keyword><keyword><style  face="normal" font="default" size="100%">water quality (voyant)</style></keyword></keywords><dates><year><style  face="normal" font="default" size="100%">2006</style></year></dates><publisher><style face="normal" font="default" size="100%">Springer Netherlands</style></publisher><pages><style face="normal" font="default" size="100%">527-547</style></pages><language><style face="normal" font="default" size="100%">eng</style></language><abstract><style face="normal" font="default" size="100%">Desertification is the consequence of a series of important processes in the Mediterranean environments, especially in semi-arid and arid regions, where water is the main limiting factor of land use performance on ecosystems. Among the most important processes of desertification are soil erosion and salinization particularly affecting hilly areas and lowlands, respectively. Various methodologies have been developed in identifying and mapping environmentally sensitive areas (ESAs) to desertification. Studies have shown that the various types of ESAs have different behavior on crop production, plant growth, grazing capacity, and soil erosion rates. For example, olive oil and cereal production decreased as the type of ESA changes from non-threatened to critical areas. Soil erosion measures have shown that soil erosion rates increased as the sensitivity of land to desertification increased. Loss in land productivity greatly affects farmer’s income and measures applied for protecting the land from further degradation and desertification. The necessity of elaborating indicators is one of the priorities identified by the United Nations Convention to Combat Desertification (UNCCD). The use of indicators can generally simplify complex processes and provide appropriate tools for combating desertification. Indicators can be classified to those related a) to the physical environment (soil, vegetation, climate), b) to the land management (tillage operations, irrigation practices, animal density grazing the land, forest fire protection, erosion measures, etc), and c) to the socio-economic characteristics (farmer age, family size, farm size, subsidies, farmer income, etc). Indicators can be better used for defining land desertification risk if they are classified according to the land use type. For example important indicators for defining desertification risk for vineyards are related to land management as well as to land characteristics such as tillage operations, tillage direction, slope gradient, parent material, plant cover, etc. Studies, conducted in areas in which the main process of desertification was salinization, showed that important indicators for defining desertification risk were ground water depth, drainage, water quality, frequency of flooding, distance from the seashore, type of land use, rainfall, etc.</style></abstract></record><record><source-app name="Biblio" version="7.x">Drupal-Biblio</source-app><ref-type>5</ref-type><contributors><authors><author><style face="normal" font="default" size="100%">Kosmas, C.</style></author><author><style face="normal" font="default" size="100%">Tsara, M.</style></author><author><style face="normal" font="default" size="100%">Moustakas, N.</style></author><author><style face="normal" font="default" size="100%">Kosma, D.</style></author><author><style face="normal" font="default" size="100%">Yassoglou, N.</style></author></authors><secondary-authors><author><style face="normal" font="default" size="100%">Kepner, W. G.</style></author><author><style face="normal" font="default" size="100%">Rubio, Jose L.</style></author><author><style face="normal" font="default" size="100%">Mouat, David A.</style></author><author><style face="normal" font="default" size="100%">Pedrazzini, F.</style></author></secondary-authors></contributors><titles><title><style face="normal" font="default" size="100%">PART . VI Desertification Indicators and Forecasting Techniques ENVIRONMENTALLY SENSITIVE AREAS AND INDICATORS OF DESERTIFICATION</style></title><secondary-title><style face="normal" font="default" size="100%">Desertification in the Mediterranean Region a Security Issue</style></secondary-title></titles><keywords><keyword><style  face="normal" font="default" size="100%">desertification indicators</style></keyword><keyword><style  face="normal" font="default" size="100%">land management</style></keyword><keyword><style  face="normal" font="default" size="100%">land use type</style></keyword><keyword><style  face="normal" font="default" size="100%">soil erosion</style></keyword><keyword><style  face="normal" font="default" size="100%">water quality (voyant)</style></keyword></keywords><dates><year><style  face="normal" font="default" size="100%">2006</style></year><pub-dates><date><style  face="normal" font="default" size="100%">2006///</style></date></pub-dates></dates><publisher><style face="normal" font="default" size="100%">Springer Netherlands</style></publisher><pages><style face="normal" font="default" size="100%">527 - 547</style></pages><language><style face="normal" font="default" size="100%">eng</style></language><abstract><style face="normal" font="default" size="100%">Desertification is the consequence of a series of important processes in the Mediterranean environments, especially in semi-arid and arid regions, where water is the main limiting factor of land use performance on ecosystems. Among the most important processes of desertification are soil erosion and salinization particularly affecting hilly areas and lowlands, respectively. Various methodologies have been developed in identifying and mapping environmentally sensitive areas (ESAs) to desertification. Studies have shown that the various types of ESAs have different behavior on crop production, plant growth, grazing capacity, and soil erosion rates. For example, olive oil and cereal production decreased as the type of ESA changes from non-threatened to critical areas. Soil erosion measures have shown that soil erosion rates increased as the sensitivity of land to desertification increased. Loss in land productivity greatly affects farmer’s income and measures applied for protecting the land from further degradation and desertification. The necessity of elaborating indicators is one of the priorities identified by the United Nations Convention to Combat Desertification (UNCCD). The use of indicators can generally simplify complex processes and provide appropriate tools for combating desertification. Indicators can be classified to those related a) to the physical environment (soil, vegetation, climate), b) to the land management (tillage operations, irrigation practices, animal density grazing the land, forest fire protection, erosion measures, etc), and c) to the socio-economic characteristics (farmer age, family size, farm size, subsidies, farmer income, etc). Indicators can be better used for defining land desertification risk if they are classified according to the land use type. For example important indicators for defining desertification risk for vineyards are related to land management as well as to land characteristics such as tillage operations, tillage direction, slope gradient, parent material, plant cover, etc. Studies, conducted in areas in which the main process of desertification was salinization, showed that important indicators for defining desertification risk were ground water depth, drainage, water quality, frequency of flooding, distance from the seashore, type of land use, rainfall, etc.</style></abstract><notes><style face="normal" font="default" size="100%">The following values have no corresponding Zotero field:&lt;br/&gt;periodical: Desertification in the Mediterranean Region a Security Issue</style></notes></record><record><source-app name="Biblio" version="7.x">Drupal-Biblio</source-app><ref-type>17</ref-type><contributors><authors><author><style face="normal" font="default" size="100%">Pardini, Giovanni</style></author><author><style face="normal" font="default" size="100%">Gispert, Maria</style></author><author><style face="normal" font="default" size="100%">Dunjó, Gemma</style></author></authors></contributors><titles><title><style face="normal" font="default" size="100%">Runoff erosion and nutrient depletion in five Mediterranean soils of NE Spain under different land use.</style></title><secondary-title><style face="normal" font="default" size="100%">The Science of the total environment</style></secondary-title></titles><keywords><keyword><style  face="normal" font="default" size="100%">Abandonment</style></keyword><keyword><style  face="normal" font="default" size="100%">erosion</style></keyword><keyword><style  face="normal" font="default" size="100%">land management</style></keyword><keyword><style  face="normal" font="default" size="100%">nutrient availability</style></keyword><keyword><style  face="normal" font="default" size="100%">Nutrient losses</style></keyword><keyword><style  face="normal" font="default" size="100%">runoff</style></keyword><keyword><style  face="normal" font="default" size="100%">Sediment yield</style></keyword><keyword><style  face="normal" font="default" size="100%">soil properties</style></keyword><keyword><style  face="normal" font="default" size="100%">structure</style></keyword><keyword><style  face="normal" font="default" size="100%">Water retention</style></keyword></keywords><dates><year><style  face="normal" font="default" size="100%">2003</style></year></dates><volume><style face="normal" font="default" size="100%">309</style></volume><pages><style face="normal" font="default" size="100%">213-224</style></pages><language><style face="normal" font="default" size="100%">eng</style></language><abstract><style face="normal" font="default" size="100%">We investigated the influence of agricultural management and various plant covers related to the period of abandonment on soil properties, erosion and nutrient depletion in a typical Mediterranean area with sandy loam shallow soils. Cultivated soils (CS) with insufficient management, 5 year abandoned soils covered with meadow (A5), 25 year abandoned soils covered with dense scrubs (A25), 50 year abandoned soils covered with cork trees (A50) and soils in a 50 year pine reforested area (P50) were studied over a period of 6 months (May-October 1999). The soils were classified as Lithic Xerorthents. Both the differences in soil properties and response to rainfall events were mainly attributed to the different vegetation types and stages in land management. Principal components analysis (PCA) was performed on the results, by running the overall data determined after five rainfall events. The factors extracted by PCA of the samples by variables matrix represented the response of the environments to different rainfall intensities as a function of management or natural evolution after abandonment. CS environments showed the highest runoff and sediment yield as well as the highest amount of dissolved organic carbon (DOC) and nitrogen in runoff water. The sequence of abandonment (A5, A25 and A50) showed approximately the same runoff production, whereas eroded sediments (ES) and DOC were inversely correlated. Organic carbon in the ES and DOC in runoff water always increased with the period of abandonment, which accounted for consistent nutrient depletion. Nevertheless, the A50 environment (dominated by Quercus suber) showed the best soil properties, whilst the A25 environment with dense cover of Cistus monspeliensis and Calicotome espinosa seemed to cause a worsening effect on the soil's physical and chemical properties. This is probably because these environments are more severely damaged by wild fire occurrence. In terms of sediment yield, the P50 environment followed CS environment, indicating that reforestation followed by insufficient forest management may negatively affect both soil properties and response to the erosive action of rainfall.</style></abstract><accession-num><style face="normal" font="default" size="100%">12798105</style></accession-num></record><record><source-app name="Biblio" version="7.x">Drupal-Biblio</source-app><ref-type>17</ref-type><contributors><authors><author><style face="normal" font="default" size="100%">Pardini, Giovanni</style></author><author><style face="normal" font="default" size="100%">Gispert, Maria</style></author><author><style face="normal" font="default" size="100%">Dunjó, Gemma</style></author></authors></contributors><titles><title><style face="normal" font="default" size="100%">Runoff erosion and nutrient depletion in five Mediterranean soils of NE Spain under different land use.</style></title><secondary-title><style face="normal" font="default" size="100%">The Science of the total environment</style></secondary-title></titles><keywords><keyword><style  face="normal" font="default" size="100%">Abandonment</style></keyword><keyword><style  face="normal" font="default" size="100%">erosion</style></keyword><keyword><style  face="normal" font="default" size="100%">land management</style></keyword><keyword><style  face="normal" font="default" size="100%">nutrient availability</style></keyword><keyword><style  face="normal" font="default" size="100%">Nutrient losses</style></keyword><keyword><style  face="normal" font="default" size="100%">runoff</style></keyword><keyword><style  face="normal" font="default" size="100%">Sediment yield</style></keyword><keyword><style  face="normal" font="default" size="100%">soil properties</style></keyword><keyword><style  face="normal" font="default" size="100%">structure</style></keyword><keyword><style  face="normal" font="default" size="100%">Water retention</style></keyword></keywords><dates><year><style  face="normal" font="default" size="100%">2003</style></year><pub-dates><date><style  face="normal" font="default" size="100%">2003///</style></date></pub-dates></dates><urls><web-urls><url><style face="normal" font="default" size="100%">http://www.ncbi.nlm.nih.gov/pubmed/12798105</style></url></web-urls></urls><volume><style face="normal" font="default" size="100%">309</style></volume><pages><style face="normal" font="default" size="100%">213 - 224</style></pages><language><style face="normal" font="default" size="100%">eng</style></language><abstract><style face="normal" font="default" size="100%">We investigated the influence of agricultural management and various plant covers related to the period of abandonment on soil properties, erosion and nutrient depletion in a typical Mediterranean area with sandy loam shallow soils. Cultivated soils (CS) with insufficient management, 5 year abandoned soils covered with meadow (A5), 25 year abandoned soils covered with dense scrubs (A25), 50 year abandoned soils covered with cork trees (A50) and soils in a 50 year pine reforested area (P50) were studied over a period of 6 months (May-October 1999). The soils were classified as Lithic Xerorthents. Both the differences in soil properties and response to rainfall events were mainly attributed to the different vegetation types and stages in land management. Principal components analysis (PCA) was performed on the results, by running the overall data determined after five rainfall events. The factors extracted by PCA of the samples by variables matrix represented the response of the environments to different rainfall intensities as a function of management or natural evolution after abandonment. CS environments showed the highest runoff and sediment yield as well as the highest amount of dissolved organic carbon (DOC) and nitrogen in runoff water. The sequence of abandonment (A5, A25 and A50) showed approximately the same runoff production, whereas eroded sediments (ES) and DOC were inversely correlated. Organic carbon in the ES and DOC in runoff water always increased with the period of abandonment, which accounted for consistent nutrient depletion. Nevertheless, the A50 environment (dominated by Quercus suber) showed the best soil properties, whilst the A25 environment with dense cover of Cistus monspeliensis and Calicotome espinosa seemed to cause a worsening effect on the soil's physical and chemical properties. This is probably because these environments are more severely damaged by wild fire occurrence. In terms of sediment yield, the P50 environment followed CS environment, indicating that reforestation followed by insufficient forest management may negatively affect both soil properties and response to the erosive action of rainfall.</style></abstract><issue><style face="normal" font="default" size="100%">1-3</style></issue><notes><style face="normal" font="default" size="100%">The following values have no corresponding Zotero field:&lt;br/&gt;accession-num: 12798105</style></notes></record></records></xml>