myb23(2)-552

Land use and land cover dynamics in the dehesa of Sierra Morena Biosphere Reserve (Sierra Norte de Sevilla Natural Park, Spain), 1956-2007

Dinámica del uso y cobertura del suelo en las dehesas de Sierra Morena (Parque Natural Sierra Norte de Sevilla, España), 1956-2007

Juan Manuel Mancilla-Leytón1*, Antonio Puerto-Marchena1 and Ángel Martín-Vicente1

1 Universidad de Sevilla. Departamento Biología Vegetal y Ecología. Sevilla, España.

* Corresponding author. jmancilla@us.es

Abstract

The dehesa, a representative savanna-like ecosystem type, has played and plays an important economic, ecological and social role, in addition to the valuable environmental services that it provides. The present study is focused on the analysis of the changes in the land use /cover of the dehesa in the Sierra Norte de Sevilla Natural Park (Sierra Morena Biosphere Reserve) during the last 50 years. In order to estimate the consequences that the change of land uses and, the activities that are carried out on it have on the dynamics of the dehesa, a diachronic analysis was performed for the period 1956-2007 using the digital geographic information available. The most important changes observed were related to: i) the increase of urban areas, water surface area, reforestation areas, eroded areas, mining areas and dumping sites; and ii) the decrease of cultivation areas, dehesa, scrubland and pastureland. The changing dynamics did not strictly respond only to phytosociological aspects, but it is necessary to explain the evolution of the landscape from the complex balance between biophysical and socioeconomic dynamics, where the current environmental changes also make it very difficult to ensure the persistence of this ecosystem. The present legislation promotes the development of a clear and up-to-date diagnosis of the problems that this ecosystem is facing. In this sense, the geographic information systems may be very useful at establishing the guidelines for the conservation and regeneration of the dehesas, and at spreading their environmental values.

Keywords: conservation, GIS, global change, environmental sciences, environmental values, regeneration.

Resumen

La dehesa, además de los valiosos servicios ambientales que presta, ha jugado y juega un importante papel económico, ecológico y social. En el presente estudio se analizan los cambios en el uso y cubierta del suelo de las dehesas en el Parque Natural Sierra Norte de Sevilla (Sierra Morena) durante los últimos 50 años. Se realizó un análisis diacrónico para el período 1956-2007 utilizando la información geográfica digital disponible. Los cambios más importantes observados estuvieron relacionados con: i) el incremento de las áreas urbanas, la superficie del agua, áreas de reforestación, áreas erosionadas, áreas de minería y vertederos; y ii) la disminución de las áreas de cultivo, de dehesa, de monte bajo y pastos. Las dinámicas encontradas no respondieron exclusivamente a los aspectos fitosociológicos, pero fueron necesarias para explicar la evolución del paisaje desde el complejo equilibrio entre las dinámicas biofísicas y socioeconómicas, donde también los actuales cambios ambientales hacen que sea muy difícil asegurar la persistencia de este particular ecosistema. La actual legislación promueve el desarrollo de un diagnóstico claro de los problemas que este ecosistema enfrenta. En este sentido, los sistemas de información geográfica pueden ser muy útiles en el establecimiento de las directrices para la regeneración y conservación de las dehesas, y en el énfasis de sus valores ambientales.

Palabras clave: conservación, SIG, cambio global, ciencia medioambiental, valores ambientales, regeneración.

Introduction

In Andalucía, the dehesas, a representative savanna-like ecosystem type, comprise vast land areas (1 263 143 ha, a third part of the total coverage), and also in other Spanish counties (mainly Extremadura, Castilla-La Mancha and Castilla-León), and in Portugal (known as montados) (Silva and Ojeda, 1997; Silva, 2010). This ecosystem, that derives from a long history of human transformation of Mediterranean forests through clearing, browsing and ploughing to provide food for livestock rearing, are composed of an overstorey of scattered oaks (mainly holm-oak and secondary Q. suber L. cork oak), at 20 trees/ha – 30 trees/ha, and an annual grasslands layer (Leiva, Mancilla-Leytón and Martín-Vicente et al., 2015). Shrubs interspersed in the grassland matrix may also occur but they are usually confined to less transformed and intensively grazed patches, usually dedicated to wild game. This ecosystem is not only one of the most representative landscapes of the Iberian Peninsula (3.3 million of hectares – 3.5 million of hectares, according to the Second National Forest Inventory) of great aesthetical, recreational and cultural value (Leiva et al., 2015), but it also shows great relevance regarding the way its resources can be used, favoring production and conservation jointly (Fernández-Alés, 1999; Costa, Martín-Vicente, Fernández-Alés and Estirado et al., 2006). It is a multifunctional exploitation system (agro-forest-pastoral), highly sustainable (scarce inputs and few residues), with which some human communities of the western and southwestern part of the Iberian Peninsula have responded to a set of geoedaphic, biogeographic, economic and social circumstances (Martín-Vicente and Fernández-Alés, 2006). The dehesa plays an important economic, ecological and social role, since, besides providing agricultural, livestock and forest productions to maintain some stable populations and the market, it also performs a set of environmental services such as the conservation of biodiversity (habitat for many species and communities of flora and fauna), the regulation of the water and carbon cycles, protection of soil against erosion or forest fire prevention by acting as firewalls (Costa et al., 2006; Anaya-Romero, Muñoz-Rojas, Ibáñez and Marañon, 2016).

Between the 60s and 80s there was a decrease of the land area assigned to dehesas due to the swine fever, the abandonment of rural habitat and the increase of new ways of agricultural production (Martín-Vicente and Fernández-Alés, 2006). In the last decade, what remains from this ecosystem is in decay and the need for improving the regeneration of trees in the dehesas is an imperative feature acknowledged by the administrations, and it is considered in the recent Andalusian regulations (Law 7/2010, of 14th July, for the Dehesa, BOJA 144), in the less recent regulations of Extremadura (Law 1/1986, of 2nd May, about the Dehesa in Extremadura) and in the background documents for planning the management of the dehesas at a ministerial level (Pulido et al., 2010).

One of the main signs of this decay is the alarming lack of regeneration of trees in a large part of the dehesas of the national territory, with populations of old holm oaks where young individuals are scarce or do not exist (Siscart, Diego and Lloret, 1999; Pulido and Díaz, 2005; Leiva et al., 2015). This phenomenon, due mainly to the rural exodus, which involves the abandonment of the exploitation management, and to the lack of maintenance abilities and skills (“loss of the traditional know-how-to”), becomes worse by the impact of health problems in the trees (“forest decay syndrome” or “drying”) which affects many of the dehesas in Andalusia and other counties (see Natalini, Alejano, Vázquez-Piqué, Cañellas and Gea-Izquierdo, 2016) and endangers the persistence of these systems at the medium and long term. However, the probable impact that these processes may be causing on the evolution of the spatial occupation of the dehesa (its reduction, expansion or territorial stability) in a certain region has not been considered in detail, perhaps due to the difficulty of integrating both study scales.

The present Law of the Dehesa in Andalusia promotes the development of a clear and recent diagnosis of the problems that could set the guidelines for its conservation, regeneration and spreading of its environmental values. Given this imperative need, and there are few studies focused on this issue, it is necessary to evaluate and know the temporal dynamics of the use of holm oak area land in the last few decades. So, in the present study, the temporal dynamics of the land use/cover as dehesa was estimated for the last 50 years, through a diachronic study carried out in Sierra Norte de Sevilla Natural Park (Dehesas de Sierra Morena Biophere Reserve, Spain).

Material and methods

Study area

The study was focused on Sierra Norte de Sevilla Natural Park (37º 40 N, 5º 59 W), western Andalucía (Southern Spain). Sierra Norte de Sevilla Natural Park (177 000 ha), Aracena y Picos de Aroche Natural Park and Sierra de Hornachuelos Natural Park were declared “Dehesas de Sierra Morena” Biosphere Reserve by the United Nations Educational, Scientific and Cultural Organization (Unesco), in November 2002 (Villa and Hernández de la Obra, 2003). It is the largest Biosphere Reserve in the Iberian Peninsula dedicated to the dehesa as a representative landscape of the Mediterranean region. The study area is a mid-mountain region, where dehesas, scrublands, forests and marginal crops create an exceptional mosaic of landscapes. The climate is Mediterranean, with an average annual rainfall between 600 mm and 950 mm and an average annual temperature between 13.4 °C and 17.6 ºC. The rain falls mainly between mid-September and mid-May and it is not significant during the summer.

Analysis of the changing processes of land use /land cover

The spatial analysis of information has recently turned a greatly important aspect in science for the knowledge of natural and/or anthropic phenomena (diagnosis performance; generation of guidelines for zoning; support for decision-making, etc.). The increasing awareness about the adverse effects of the breaking-up of the habitats established on the natural systems has fostered an increasing demand on instruments to predict and evaluate the effect that management projects and important infrastructure constructions may have in the connectivity of the natural world (Adriaensen, Chardon and De Blust, 2003).

The landscapes, as every ecological unit, are dynamic in structure, function and spatial pattern. This dynamic condition of the landscape requires time, or temporal changes, to be considered in the quantitative studies. In this framework of dynamic interrelationships among the economic systems and the environmental and social systems of the dehesa, the use of cartography, and more specifically the use of Geographic Information Systems (GIS), has become an instrument of great value (fast and economic) that allows analyzing the changes diachronically.

In order to analyze the temporal dynamics of the land use/cover of the Sierra Norte de Sevilla Natural Park, a diachronic study was carried out. A necessary graphic (maps) and computerized (handling of databases and applications) environment was generated to make it possible to interpret the geographic digital information available, which was named Project ArcMap (Environmental Systems Research Institute [ESRI], 2008).

To make the different maps of changes of use, background cartographic information was employed, which was later processed. For the selection of the borderline of the Sierra Norte de Sevilla Natural Park, the layer of information from Red Natura 2000 in Andalusia was used, in shape format, at a detail and recognition scale (at a scale of 1:10 000, 2008). The Land Use and Land Cover Map of Andalusia (LULCMA) for 1956, 1999, 2003 and 2007 (at a scale of 1:25 000) was used as a base (Moreira, 2007). The LULCMA was a result of the Coordination of Information on the Environment (Corine) programme of the European Commission. Corine project offers stable information on land cover and land cover changes across Europe (Muñoz-Rojas et al., 2015). The special reference systems (coordinates systems, map projections, etc.) used in maps was EPSG 23030 (ED 50 / UTM Zone 30N).

This information, in shape format, was reclassified according to similarity criteria between each one of the uses following the expert bibliography consulted, with the aim of making it easier to handle the information and highlighting the land uses/cover that may be truly interesting in this study. The classification of the forest covers was performed regarding the tree species that were predominant in the uses. The “forest areas and natural wooded areas with predominant dense wooded formations” were grouped according to the three predominant plant species, differentiating: i) Dehesas: forest and natural areas with predomination of some generally long life-cycle species of Quercus; ii) Forests: forest and natural areas with predomination of some middle-short life-cycle species (Conifers and Eucalyptus). In this way, the number of groups of uses was reduced from 112 to 12: urban, communication routes, mining areas, water surface areas, crops, dehesas, scrublands, grasslands, reforestation, all other vegetation, eroded areas and dumping sites (Table 1).

Table 1. Reclassification of land use and land cover types of Andalusia.

Reclassification

Codes for use and land cover types *

1

Urban

111, 115, 117, 121, 131, 133, 135, 137 ,141, 151, 153, 155,157, 191, 193, 221, 225

2

Communication routes

131

3

Water surface areas

311, 321, 331, 341, 345

4

Mining areas

151

5

Crops

411, 441, 479, 891, 895, 415, 417, 419, 481, 445, 489, 423, 431, 430, 439, 433, 475, 477, 427, 425, 451, 461, 465, 471, 473

6

Dehesas

510, 611, 615, 711, 715, 811 ,815

7

Reforestation

520, 550, 621, 625, 650, 721, 725, 750, 821, 825, 850, 570, 530, 560, 630, 660, 670, 730, 760, 770, 830, 860, 870

8

Scrublands

911, 915, 917

9

Grasslands

925, 932

10

Other vegetation

540, 580, 640, 680, 740, 780, 840, 880

11

Eroded areas

901, 934, 935

12

Dumping sites

153, 157

* From the Land Use and Land Cover Map of Andalusia (Moreira, 2007)

Results

Table 2 and figure 1 show the results obtained from the diachronic analyses of the land use /cover. Together, the great changes of land use occurred between 1956 and 1999, being lower during the last few years (2003 and 2007). The clear, most important changes observed were related to: the increase of urban areas; water surface area; reforestation areas; eroded areas; mining areas and dumping sites; and to the decrease of cultivation areas, dehesas, scrubland and grassland.

A

B

Figure 1. Map of Sierra Norte de Sevilla Natural Park by category of use / vegetation cover soil in 1956 (A), 1999 (B), 2003 (C) and 2007 (D). (part 1 of 2).

D

C

Figure 1. Map of Sierra Norte de Sevilla Natural Park by category of use / vegetation cover soil in 1956 (A), 1999 (B), 2003 (C) and 2007 (D). (part 2 of 2).

Table 2. Gain and/or loss (Ha) of Sierra Norte of Sevilla Natural Park by category of use / vegetation cover the soil in the years 1956, 1999, 2003 and 2007.

Category

1956-1999

1956-2003

1956-2007

Communication routes

0.2

0.5

0.5

Water surface areas

1197.4

1168.0

1295.3

Crops

-1328.2

-969.5

-1385.5

Dehesa

-2443.5

-2938.1

-2072.8

Scrublands

-6614.8

-6496.0

-4920.4

Grasslands

129.9

-9.9

-1756.0

Reforestation

8389.5

7731.3

8259.4

Other vegetation

340.1

344.4

149.3

Urban areas

143.7

157.7

190.8

Dumping sites

9.7

9.7

9.7

Eroded areas

157.2

980.1

196.9

Mining areas

18.9

22.3

32.0

Within the period of 1956-1999 urban surface area increased 58% (144 ha), affecting farming and forest areas (Figs. 1A and B). During more recent periods, urban area, far from stopping, was expanding (4% for the period 1999-2003 and 8% for 2003-2007) (Figs. 1C and D). These increments were significant in the main populations of the Park (Cazalla de la Sierra, El Pedroso, Constantina and Las Navas de la Concepción).

The water surface areas include natural and anthropogenic (reservoirs, irrigation ponds...) ecosystems. These zones have experienced an increment of 260% (almost 2000 ha) during the period 1956-1999, and remained practically stable until 2007 (these data must be regarded with caution, as they are likely to vary among seasons) (Table 2). These increments were basically due to a sharp increase of water coverage of reservoirs, caused by the construction of the Huéznar´s Reservoir at the southern region of the Park, and the Retortillo´s Reservoir, southeast, which are added up to the already existing. El Pintao´s Reservoir at the north, affecting the cultivation areas, dehesas, scrubland and pastureland (Fig. 1).

Reforestations (conifers and eucalyptus) show great increase in the period 1956-1999 (8390 ha, approximately an increase of 3250%), from which there was a slight decrease in 2003 (-700 ha), and was established later within the same values of 1999 in 2007 (Table 2). These new reforested tree masses have substituted mostly dehesa and scrubland areas, being this change significant in the southeastern and southwestern areas of the Park (Fig. 1).

The creation of new dumping sites (almost 10 ha), boosted by the increment of urban zones, as well as the increment of eroded areas (especially during the period 1956-2003, more than 900 ha) and the 400% increase of the mining areas (El Cerro del Hierro) from 1956 to 2007, are examples of surface degradation derived from anthropic activities.

The increments of uses were obvious; however, the decreases were even more obvious. As it was previously mentioned, during the period 1956-1999, an important reduction was observed in plant formations such as the scrubland (-6615 ha) and the dehesa (-2443 ha). Likewise, there was also a decrease in the use of crops (-1328 ha). This pattern remains obvious in the period 1956-2003; the loss of land as dehesa becoming even more obvious (-2938 ha) (Table 2; Figs. 1A and B). In the period 2003-2007, the decrease of uses of grassland areas (-1746 ha), cultivation areas (-416 ha) and eroded areas was related to an increase of scrubland areas (1576 ha), dehesa areas (865 ha) and reforestation areas (528 ha) (Table 2; Figs. 1C and D).

The results obtained allow us to perform a detailed “loss and gain” study for each period (Figs. 2 and 3). If we only focus on the use of the dehesa, the data show an important surface loss with time: 9093 ha in the year 1999 (very obvious in the southeastern and southwestern regions of the Park), 9794 ha in the year 2003 and 10 054 ha in the year 2007 with respect to the land use/cover in the year 1956 (Figs. 2 and 3). However, this loss was balanced with gains (reforestations), which were 6650 ha in the year 1999, 6857 ha in 2003 and 7982 ha in 2007 (very obvious in the northeastern region) with respect to the land use/cover in the year 1956 (Figs. 2 and 3). Therefore, there was a “loss” or negative balance (more than 2000 ha) in the period 1956-2007 (Table 2).

A

B

C

Figure 2. Map of the dynamic of the dehesa of Sierra Norte of Sevilla Natural Park from use / vegetation cover the soil in 1956-1999 (A), 1999-2003 (B) and 2003-2007 (C).

Figure 3. Gain, loss and balance of land use as dehesa for different periods in the Sierra Norte de Sevilla Natural Park.

Discussion

The results found in the present study showed that the process of change of land uses, consisting of the abandonment of the primary economic activities and the substitution for residential uses or even the absence of uses, represents the transition of an agricultural model, characterized by the subsistence farming (rain-fed, irrigation or under plastic) and the forest exploitation of wood and wood-fuels (conifers and eucalyptus), to a postindustrial model, typically outsourced (tourism). These processes, together with the current processes of complex environmental change (influence of light, orography, predation, scrubland expansion, senescence, phytosanitary state, etc.) make it very difficult to ensure the persistence of this ecosystem (dehesa).

The Andalusian forest surface has been subjected to many operations since man came to this land; the clearing of forests for the expansion of cultivations, the use of wood to supply the metal industry, the grazing, the extraction of wood for the construction of ships and houses and even the burning of forests in several wars have formed the present forest landscape of Andalucía (Emanuelsson, 2009). The economic development experienced by the western countries in the last 50 years has triggered an important change in land use/cover. In the mid-nineteenth century, as a consequence of the confiscations, the most intense process of forest resource appropriation takes place; more than 430 000 ha of mount were alienated in Andalucía, most of these immediately transformed in order to obtain a quick benefit from wood sales (Ojeda, 2013). The use of the most fertile areas has been intensified, at the same time as the marginal areas have been greatly abandoned, which has changed the structure and functioning of the landscapes (Fernández-Alés, Martín-Vicente, Ortega and Alés, 1992; Grove and Rackham, 2001; Ojeda, 2013). In the first study period, 1956-1999, the crisis of the traditional agricultural system of the mountainous region caused a decrease of the competitiveness of livestock exploitations, structural unemployment, emigration, regression and aging of the population and, consequently, the landscape and environmental change, reflected by the abandonment of the dehesas and cultivation lands, the advance of the scrubland and the appearance of fast-growing forest crops (conifers and eucalyptus) (Ojeda, 2013).

If in this first period traditional exploitation such as improper pruning (charcoaling) and removal of scrubland were the main causes that affected negatively the survival and recruitment of trees in the dehesa (Martín-Vicente and Fernández-Alés, 2006), the modern uses (farming, introduction of crops, as irrigation, intensive livestock breeding, reforestations, construction of new reservoirs...) may be the triggers of the greatest loss of dehesas area until 2003 (also 3000 ha in the period 1956-2003, Table 2), besides being related to the restrictions applied to forest practices in this territory, and perhaps also related to the fact that the investments made in the area were assigned with priority to the tourism sector more than to the recovery of grasslands, dehesas and native vegetation (Álvarez-Carriazo, 2002). Likewise, the abandonment of the marginal, poorly profitable crops and the general depopulation of the rural areas (causing an important urban growth, Table 2), fostered to some extent by the system of community grants carried out in the last few decades, has favored an increase of forest fires, which has resulted in an important decrease of the area occupied by natural vegetation (decreasing scrubland or coppice and dehesa formations, with respect to the previous period studied, while increasing the land occupied by herbaceous formations and reforestations of conifers and eucalyptus).

By last, in the study period 2003-07, the statement of the UNESCO in 2002 “Dehesas de Sierra Morena” Biosphere Reserve has apparently changed this tendency, contributing to a decrease in the uses of grasslands, cultivation areas and eroded areas towards an increase of scrublands, dehesas and reforestation areas, with respect to the year 2003 (Table 2, Fig. 2). This is a change in the concept of landscape, by which dynamism clearly substitutes immobility and landscapes are regarded as life spaces (Ojeda and Silva, 2002; Silva, 2010).

Future Prospects and Implications

In the present study, based on the reported processes of changes of land use/cover, the unidisciplinary interpretations were insufficient for interpreting the current landscape of the dehesa in the interval 1956-2007. The change dynamics does not strictly respond only to phytosociological aspects; it is also necessary to explain the landscape evolution from the complex equilibrium between biophysical and socioeconomic dynamics (Gómez-Aparicio, Pérez-Ramos and Mendoza, 2008).

Many studies state that, within the last few decades, the dehesa has decreased dramatically not only in Andalusia, but also in the rest of the Iberian Peninsula (Silva, 2010; Bugalho, Caldeira, Pereira, Aronson and Pausas, 2011). The dehesa has experienced a change of uses, evolving in most cases through the boost of intensive agriculture, or by the abandonment of agricultural activities and the boost of hunting activities, or through forest cultivation of fast-growth species. Besides the actual loss of land use as a dehesa, the current tree population of the dehesa is far from the favorable conservation state required by the Habitat Directive; the density and state of the trees are unsatisfactory (old age and phytosanitary problems, the “drying”), as well as the conservation state of several species linked to the dehesas (Ferraz-de-Oliveira, Azeda and Pinto-Correia, 2016).

For all this, the management of the dehesa must be focused on the maintenance of an optimal production that can be combined with the conservation of the system at the long term, since most of the traditional rural activities, based on the transmission of success and exclusion of mistakes, have been lost and the active population that keeps the dehesa under use has become old (Law of the Dehesa 7/2010, Green Paper of the Dehesa 2010). In this sense, studies such as the present one may approach, clarify and develop the most adequate sites and techniques, from the economic and ecological perspectives, that ensure the future of the dehesa.

Acknowledgments

The authors wish to thank Juan Carlos Costa for the logistic support and field facilities. We also thank Juan Francisco Ojeda and José Torres for their useful comments on the early version of this manuscript. This study partially was funded by grants from the Consejería de Medio Ambiente (Junta de Andalucía) (OG-039/04). Dra. Fernández lo Faso revised the English of this text. J.M. Mancilla-Leytón gratefully acknowledges the receipt of a Postdoctoral Research Contract (V Plan Propio de Investigación de la Universidad de Sevilla, Ref. II.5.B/2015).

References

Adriaensen, F., Chardon J. P. and De Blust, G. (2003). The application of ‘least-cost’ modelling as a functional landscape model. Landscape and Urban Planning, 64(4), 233-247. doi: 10.1016/S0169-2046(02)00242-6

Álvarez C., J. L. (2002). La reforma de la contabilidad en España. Estudios financieros. Review contributation, 232, 219-246.

Anaya-Romero, M., Muñoz-Rojas, M., Ibáñez, B. and Marañón, T. (2016). Evaluation of forest ecosystem services in Mediterranean areas. A regional case study in South Spain.Ecosystem Services, 20, 82-90. doi: 10.1016/j.ecoser.2016.07.002

Bugalho, M. N., Caldeira, M. C., Pereira, J. S., Aronson, J. and Pausas, J. G. (2011). Mediterranean cork oak savannas require human use to sustain biodiversity and ecosystem services. Frontiers in Ecology and the Environment, 9(5), 278-286. doi: 10.1890/100084

Costa P., J. C., Martín-Vicente, Á. Fernández-Alés, R. y Estirado O., M. (2006). Dehesas de Andalucía. Caracterización ambiental. Sevilla, España: Consejería de Medio Ambiente Junta de Andalucía.

Emanuelsson, U. (2009). The rural landscapes of Europe: how man has shaped European nature. Formas, Stockholm: Swedish Research Council Formas.

Environmental Systems Research Institute [ESRI] (2008). ArcGIS (versión 9.3) [Software de cómputo]. Redlands: ESRI.

Fernández-Alés, R., Martín-Vicente, Á., Ortega, F. and Alés, E. E., (1992). Recent changes in landscape structure and function in a Mediterranean region of SW Spain (1950-1984). Landscape Ecology, 7(1), 3-18. doi: 10.1007/BF02573953

Fernández-Alés, R., (1999). Dehesas y montados. Bases ecológicas para su gestión. Revista de Biología, 17, 147-157.

Ferraz-de-Oliveira, M. I., Azeda, C. and Pinto-Correia, T., (2016). Management of Montados and Dehesas for High Nature Value: an interdisciplinary pathway. Agroforestry Systems, 90(1), 1-6. doi: 10.1007/s10457-016-9900-8

Gómez‐Aparicio, L., Pérez‐Ramos, I. and Mendoza, I. (2008) Oak seedling survival and growth along resource gradients in Mediterranean forests: implications for regeneration in current and future environmental scenarios. Oikos, 117(11), 1683-1699. doi: 10.1111/j.1600-0706. 2008.16814.x

Grove, A. and Rackham, O, (2011). The nature of Mediterranean Europe. An ecological history. New Haven, Connecticut: Yale University Press.

Leiva, M. J., Mancilla-Leytón, J. M. and Martín-Vicente, Á. (2015). Differences in the facilitative ability of two Mediterranean shrubs on holm-oak seedling recruitment in Mediterranean savanna-forest ecosystems. Ecological Engineering, 82, 349-354. doi: 10.1016/j.ecoleng.2015.05.019

Martín Vicente, Á. and Fernández-Alés, R. (2006). Long term persistence of dehesas. Evidences from history. Agroforests system, 67(1), 19-28. doi: 10.1007/s10457-005-1110-8

Moreira, J. M. (2007). Mapa de usos y coberturas vegetales del suelo de Andalucía Escala 1/25.000. Guía Técnica. Sevilla, España: Consejería de Medio Ambiente, Junta de Andalucía.

Muñoz‐Rojas, M., Jordán, A., Zavala, L. M., De la Rosa, D., Abd‐Elmabod, S. K. and Anaya‐Romero, M. (2015). Impact of land use and land cover changes on organic carbon stocks in Mediterranean soils (1956–2007). Land Degradation & Development,26(2), 168-179. doi: 10.1002/ldr.2194

Natalini, F., Alejano, R., Vázquez-Piqué, J., Cañellas, I. and Gea-Izquierdo, G. (2016). The role of climate change in the widespread mortality of holm oak in open woodlands of Southwestern Spain. Dendrochronologia, 38, 51-60. doi: 10.1016/j.dendro.2016.03.003

Ojeda R., J. F. (2013). Claves comprensivas de los paisajes andaluces.Revista de Estudios Regionales, 1, 21-31.

Ojeda R., J. F. and Silva P., R. (2002). Efectos de la implantación del modelo agroambiental y productivista en la Sierra Morena onubense. Estudios Geográficos, 63(246), 69-100. doi: 10.3989/egeogr.2002.i246.261

Pulido, F. J. and Díaz, M. (2005). Regeneration of a Mediterranean oak: a whole-cycle approach. Ecoscience, 12(1), 92-102. doi: 10.2980/i1195-6860-12-1-92.1

Pulido F., Picardo, A., Campos, P., Carranza, J., Coleto, J.M., Díaz, M., Diéguez, E., Escudero, A., Ezquerra, F.J., Fernández, P., López, L., Montero, G., Moreno, G., Olea, L., Roig, S., Sánchez, E., Solla, A., Vargas, J.D., Vidiella, A., (2010). Libro verde de la dehesa. Documento para el debate hacia una estrategia ibérica de gestión, Salamanca. España: Consejería de Medio Ambiente, Junta de Castilla y León.

Silva P., R. and Ojeda R., J. F. (1997). Dehesas de Sierra Morena y políticas agroambientales comunitarias. Estudios Geográficos, 227, 203-226.

Silva P., R. (2010). La dehesa vista como paisaje cultural. Fisonomías, funcionalidades y dinámicas históricas. Ería, 82,143-157. doi: 10.17811/er.0.2010.143-157

Siscart, D., Diego, V. and Lloret, F. (1999). Acorn ecology. Ecological Studies, 137, 75-87.

Villa D., A. and Hernández de la Obra, J., (2003). Dehesas de Sierra Morena. Reserva de la biosfera. Sevilla, España: Consejería de Medio Ambiente, Junta de Andalucía.

Received: 22 June 2016.

Accepted: 2 February 2017.

This paper must be cited as:

Mancilla-Leytón, J. M., Puerto-Marchena, A. and Martín-Vicente, A. (2017). Land use and land cover dynamics in the dehesa of Sierra Morena Biosphere Reserve (Sierra Norte de Sevilla Natural Park, Spain), 1956-2007. Madera y Bosques, 23(2), 133-143. doi: 10.21829/myb.2017.232552

doi:10.21829/myb.2017.232552

Enlaces refback

  • No hay ningún enlace refback.


Copyright (c) 2017 Madera y Bosques

Licencia de Creative Commons
Este obra está bajo una licencia de Creative Commons Reconocimiento-NoComercial-CompartirIgual 4.0 Internacional.

Madera y Bosques, Vol. 23, Núm. 3, Otoño 2017, es una publicación cuatrimestral editada por el Instituto de Ecología, A.C. Carretera antigua a Coatepec, 351, Col. El Haya, Xalapa, Ver. C.P. 91070, Tel. (228) 842-1835, http://myb.ojs.inecol.mx/, mabosque@inecol.mx. Editor responsable: Raymundo Dávalos Sotelo. Reserva de Derechos al Uso Exclusivo 04-2016-062312190600-203, ISSN electrónico 2448-7597, ambos otorgados por el Instituto Nacional del Derecho de Autor. Responsable de la última actualización de este Número, Reyna Paula Zárate Morales, Carretera antigua a Coatepec, 351, Col. El Haya, Xalapa, Ver., C.P. 91070, fecha de última modificación, 23 de noviembre de 2017.

Las opiniones expresadas por los autores no necesariamente reflejan la postura del editor de la publicación.

Madera y Bosques por Instituto de Ecología, A.C. se distribuye bajo una Licencia Creative Commons Atribución-NoComercial-CompartirIgual 4.0 Internacional.

 

Licencia Creative Commons

 

 Los aspectos éticos relacionados con la publicación de manuscritos en Madera y Bosques se apegan a los establecidos en el COPE.

 

Gestionando el conocimiento