Abstract:ABSTRACT. Human practices have had an impact on Mediterranean ecosystems for millennia, particularly through agricultural and pastoral activities. Since the mid-19th century, land-use abandonment has led to the expansion of shrubland and forest, especially in the mountainous areas of the northern Mediterranean basin. Knowledge of these factors is vital to understanding present forest patterns and predicting future forest dynamics in the Mediterranean mountains. We aimed to analyze and understand how land-use a… Show more
“…These new forests are mostly rapidly growing young trees that have been able to store 9% of the total C emitted in Spain between 1986 and 2007 [148]. A parallel history has been observed in the Corsica Mountains, where forest cover has spread and where natural native forests of Q. ilex and P. pinaster Aiton have expanded against Castanea sativa Miller forests, which were previously maintained by human management but are now abandoned [149].…”
Section: Forests Versus Shrublands and Grasslandsmentioning
The increase in aridity, mainly by decreases in precipitation but also by higher temperatures, is likely the main threat to the diversity and survival of Mediterranean forests. Changes in land use, including the abandonment of extensive crop activities, mainly in mountains and remote areas, and the increases in human settlements and demand for more resources with the resulting fragmentation of the landscape, hinder the establishment of appropriate management tools to protect Mediterranean forests and their provision of services and biodiversity. Experiments and observations indicate that if changes in climate, land use and other components of global change, such as pollution and overexploitation of resources, continue, the resilience of many forests will likely be exceeded, altering their structure and function and changing, mostly decreasing, their capacity to continue to provide their current services. A consistent assessment of the impacts of the changes, however, remains elusive due to the difficulty of obtaining simultaneous and complete data for all scales of the impacts in the same forests, areas and regions. We review the impacts of climate change and other components of global change and their interactions on the terrestrial forests of Mediterranean regions, with special attention to their impacts on ecosystem services. Management tools for counteracting the negative effects of global change on Mediterranean ecosystem- services are finally discussed.
“…These new forests are mostly rapidly growing young trees that have been able to store 9% of the total C emitted in Spain between 1986 and 2007 [148]. A parallel history has been observed in the Corsica Mountains, where forest cover has spread and where natural native forests of Q. ilex and P. pinaster Aiton have expanded against Castanea sativa Miller forests, which were previously maintained by human management but are now abandoned [149].…”
Section: Forests Versus Shrublands and Grasslandsmentioning
The increase in aridity, mainly by decreases in precipitation but also by higher temperatures, is likely the main threat to the diversity and survival of Mediterranean forests. Changes in land use, including the abandonment of extensive crop activities, mainly in mountains and remote areas, and the increases in human settlements and demand for more resources with the resulting fragmentation of the landscape, hinder the establishment of appropriate management tools to protect Mediterranean forests and their provision of services and biodiversity. Experiments and observations indicate that if changes in climate, land use and other components of global change, such as pollution and overexploitation of resources, continue, the resilience of many forests will likely be exceeded, altering their structure and function and changing, mostly decreasing, their capacity to continue to provide their current services. A consistent assessment of the impacts of the changes, however, remains elusive due to the difficulty of obtaining simultaneous and complete data for all scales of the impacts in the same forests, areas and regions. We review the impacts of climate change and other components of global change and their interactions on the terrestrial forests of Mediterranean regions, with special attention to their impacts on ecosystem services. Management tools for counteracting the negative effects of global change on Mediterranean ecosystem- services are finally discussed.
“…The sweet chestnut (Castanea sativa Mill.) is one of the most managed trees in Europe and covers more than 2.5 million ha (Amorini et al 2000;Scarascia-Mugnozza et al 2000;Conedera et al 2004Conedera et al , 2016San Roman Sanz et al 2013). Palynological, anthracological, and macrofossil evidence indicates that C. sativa survived the main glacial events that occurred in favorable refuges, ranging from the west of the Iberian Peninsula to the east coast of the Black Sea-Caucasus region (Fineschi et al 2000;Conedera et al 2004;Krebs et al 2004), and it is considered a component of European temperate broadleaf forests (Conedera et al 2016).…”
& Key message Quercus secondary forests show a gradual transition toward mixed forests, with sweet chestnut (Castanea sativa) becoming increasingly abundant in the western Spanish Central System. Additionally, in chestnut-dominated stands, it shows a certain resistance to competitive displacement by Quercus pyrenaica. Our results partially refute the traditional view that C. sativa is unable to recruit in the absence of cultural inputs. & Context Sweet chestnut, Castanea sativa, is a component of European broadleaf forests and is one of the most managed trees. Due to a reduction in cultural inputs, chestnut-dominated stands tend to be invaded by other species, and it is unclear how chestnut is able to persist in natural mixed forests. & Aims Our work aimed to identity the main factors that limit the establishment of C. sativa and to analyze the recruitment and mortality processes of C. sativa trees. & Methods The age, growth ring patterns, regeneration density, and the spatial structure of trees and saplings in 11 plots in the Spanish Central System were analyzed. & Results Chestnut seedling density increased with C. sativa basal area, but transition toward the sapling stage appeared limited owing to light availability. In Quercus pyrenaica secondary forests, sparse canopies did not constrain chestnut regeneration, and in old chestnut stands, C. sativa showed a certain resistance to competitive displacement. By contrast, mixed young coppices showed a high mortality, most likely due to competition with other vigorous resprouters. & Conclusion Quercus secondary forests showed a gradual transition toward mixed forests with sweet chestnut becoming increasingly more abundant. In old stands, C. sativa is likely to persist under a gap-phase mode of regeneration. Our results partially refute the traditional view that C. sativa is unable to recruit in the absence of cultural inputs.
“…In addition to the hydrological consequences associated with substantial expansion of forests and scrub, other environmental issues occur, such as the increased risk of fire (García-Ruiz and Lana-Renault, 2011;San Román et al, 2013). The effect of fire on soil properties has also been studied (Badía and Martí, 2003;Pardini et al, 2004b), particularly the hydric effects of an ash layer covering the soil surface, where responses vary according to the severity of fire (Pereira et al, 2013), as well as those deriving from fire on water, and sediment yield on different soil types (Badía et al, 2008).…”
ABSTRACT. This study presents a joint analysis of the information from 195 field infiltration experiments, using double ring devices. The experiments were carried out in 20 contrasting types of land use, distributed across three geographic contexts (coast of NE Catalonia, an area of gentle relief in the centralPalabras clave: infiltración, ensayos con doble anillo, usos del suelo, cubierta vegetal, humedad del suelo, nordeste de España.
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