13 results on '"Nadal-Romero E"'
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2. Spatial variability of the relationships of runoff and sediment yield with weather types throughout the Mediterranean basin
- Author
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G. Desir, José María Senciales-González, Patricio Cid, Álvaro Gómez-Gutiérrez, Luis Merino-Martín, Carla Ferreira, Tíscar Espigares, Miguel A. Campo-Bescós, Albert Solé-Benet, Asunción Romero-Díaz, Julián Martínez-Fernández, Damien Raclot, Damià Vericat, Agata Novara, María Martínez-Mena, C. Le Bouteiller, Encarnación V. Taguas, Francesca Todisco, Antonio Canatário-Duarte, Luciano Mateos, Francesc Gallart, José Andrés López-Tarazón, Susana Bernal, Emmanouil A. Varouchakis, Y. Le Bissonnais, Mariano Moreno-de las Heras, Noemí Lana-Renault, A. Zabaleta, Dhais Peña-Angulo, M. Mercedes Taboada-Castro, Lea Wittenberg, Ramon J. Batalla, Vito Ferro, Susanne Schnabel, Xavier Úbeda, Victor Castillo, Matija Zorn, José Carlos González-Hidalgo, Ramón Bienes, Juan Albaladejo, M.T. Taboada-Castro, Feliciana Licciardello, C. Marín, V. Simonneaux, Óscar González-Pelayo, George P. Karatzas, H. Barhi, Roberto Lázaro, E. Roose, Jesús Rodrigo-Comino, Joan Estrany, Julián Campo, Elvira Díaz-Pereira, José Luis Rubio, Sébastien Klotz, Artemio Cerdà, Javier Casalí, Vicente Andreu, Helena Gómez-Macpherson, Nicolle Mathys, Yolanda Cantón, Estela Nadal-Romero, Teodoro Lasanta, Nicola Cortesi, Orestis Kairis, Rafael Giménez, Maria Jose Marques, María Fernández-Raga, A. Cheggour, José Damián Ruiz-Sinoga, Vincenzo Pampalone, José A. Gómez, Vincenzo Bagarello, Paloma Hueso-Gonzalez, José M. Nicolau, Ana Lucía, N. Moustakas, Costas Kosmas, M. L. Rodríguez-Blanco, Jérôme Latron, E. Gimeno, Juan F. Martínez-Murillo, Govern de les Illes Balears, Generalitat de Catalunya, Fundação para a Ciência e a Tecnologia (Portugal), Ministerio de Educación, Cultura y Deporte (España), Ministerio de Economía y Competitividad (España), European Commission, Ministerio de Ciencia, Innovación y Universidades (España), Universidad de Lleida, Ministerio de Educación y Ciencia (España), Instituto Universitario de Ciencias Ambientales (IUCA), Departamento de Geografía, University of Zaragoza, Instituto Pirenaico de Ecología (IPE), Soil and Water Conservation Research Group, Centro de Edafologia y Biologia Aplicada del Segura, Desertification Research Centre, Department of Environmental Quality and Soils, CIDE-CSIC, Department of Agricultural, Food and Forest Sciences, Università degli studi di Palermo - University of Palermo, Institut National de Recherche en Génie Rural, Eaux et Forêts de Tunisie (INRGREF), Catalan Institute for Water Research (ICRA), Faculty of Forest Sciences and Natural Resources, Universidad Austral de Chile, RIUS, Fluvial Dynamics Research Group, University of Lleida (UL), Integrative Freshwater Ecology Group, Centre d’Estudis Avançats de Blanes, Departamento Investigación Aplicada y Extensión Agraria, Instituto Madrileño de Investigación y Desarrollo Rural, Agrario y Alimentario (IMIDRA), ISFOOD Institute, Department of Projects and Rural Engineering, Universidad Pública de Navarra, School of Agriculture, Food and Rural Development, Center for GeoBioSciences, GeoTechnologies and GeoEngineering (GEOBIOTEC), Universidade da Beira Interior, Department of Agronomy (Soil Science Area), University of Almeria, Department of Geography, Soil Erosion and Degradation Research Group, Université de Valence, Laboratorio Nacional de Genómica para la Biodiversidad (LANGEBIO), Maize Genetics and Genomics Lab, CINVESTAV, Department of Earth Sciences, Centro Nacional de Supercomputación, Departamento de Ciencias de la Tierra, Departamento de Ciencias de la Vida, Unidad de Ecología, Universidad de Alcalá de Henares (UAH), Department of Geography, Mediterranean Ecogeomorphological and Hydrological Connectivity Research Team (MEDhyCON), University of the Balearic Islands (UIB), Department of Applied Chemistry and Physics, University of Leon, College of Agriculture, Research Centre for Natural Resources, Environment and Society (CERNAS), Instituto Politécnico de Coimbra, Department of Earth and Marine Sciences [Palermo], Institute of Environmental Assessment and Water Research (IDAEA), Consejo Superior de Investigaciones Científicas [Spain] (CSIC), Instituto de Agricultura Sostenible (IAS), Instituto de Agricultura, INTERRA Research Institute, University of Extremadura, Department of Environment and Planning, Earth Surface Processes Team (ESP) Centre for Environmental and Marine Studies (CESAM), University of Aveiro, Department of Natural Resources Management and Agricultural Engineering, Agricultural University of Athens, School of Environmental Engineering, Technical University of Crete, Erosion torrentielle neige et avalanches (UR ETGR (ETNA)), Institut national de recherche en sciences et technologies pour l'environnement et l'agriculture (IRSTEA), Université Grenoble Alpes (COMUE) (UGA), Area of Physical Geography, DCH, Universidad de la Rioja, Experimental Station of Arid Zones (EEZA), Consejo Superior de Investigaciones Científicas, Laboratoire d'étude des Interactions Sol - Agrosystème - Hydrosystème (UMR LISAH), Institut de Recherche pour le Développement (IRD)-Institut National de la Recherche Agronomique (INRA)-Centre international d'études supérieures en sciences agronomiques (Montpellier SupAgro)-Institut de Recherche pour le Développement (IRD [ Madagascar])-Institut national d’études supérieures agronomiques de Montpellier (Montpellier SupAgro), Department of Agriculture, Food and Environment, Department of Geography, Mediterranean Ecogeomorphological and Hydrological Connectivity Research Team (MEDhyCON) Hydrol Connect Res, Dept Geog, Palma De Mallorca 07122, Spain, Institute of Earth and Environmental Science [Potsdam], University of Potsdam, Faculty of Sciences, Center for Applied Geosciences, Eberhard Karls University Tübingen, Instituto Hispano Luso de Investigaciones Agrarias, Universidad de Salamanca, Botanique et Modélisation de l'Architecture des Plantes et des Végétations (UMR AMAP), Centre de Coopération Internationale en Recherche Agronomique pour le Développement (Cirad)-Institut National de la Recherche Agronomique (INRA)-Université de Montpellier (UM)-Centre National de la Recherche Scientifique (CNRS)-Institut de Recherche pour le Développement (IRD [France-Sud]), Institut d'Ecologie et Environnement (INEE), Centre National de la Recherche Scientifique (CNRS), Université Paul Valéry (Montpellier 3), Université de Montpellier (UM), École pratique des hautes études (EPHE), Institut de Recherche pour le Développement (IRD [Bolivie]), Centre d’Ecologie Fonctionnelle et Evolutive (CEFE), Institut de Recherche pour le Développement (IRD [France-Sud])-Centre National de la Recherche Scientifique (CNRS)-École pratique des hautes études (EPHE)-Université de Montpellier (UM)-Institut national d’études supérieures agronomiques de Montpellier (Montpellier SupAgro)-Institut National de la Recherche Agronomique (INRA)-Centre international d'études supérieures en sciences agronomiques (Montpellier SupAgro)-Université Paul-Valéry - Montpellier 3 (UM3), Instituto Universitario de Ciencias Ambientales, Escuela Politécnica Superior, Faculty of Sciences, Centre for Advanced Scientific Research (CICA), University of A Coruña (UDC), Physical Geography, Trier University, Departamento de Geografía, Universidad de Cantabria [Santander], UMR Eco&Sols, Centre d'études spatiales de la biosphère (CESBIO), Institut de Recherche pour le Développement (IRD)-Université Toulouse III - Paul Sabatier (UT3), Université Fédérale Toulouse Midi-Pyrénées-Université Fédérale Toulouse Midi-Pyrénées-Observatoire Midi-Pyrénées (OMP), Université Fédérale Toulouse Midi-Pyrénées-Centre National d'Études Spatiales [Toulouse] (CNES)-Centre National de la Recherche Scientifique (CNRS), Université Toulouse III - Paul Sabatier (UT3), Université Fédérale Toulouse Midi-Pyrénées, ETSIAM Campus Rabanales, Universidad de Cordoba, Department of Agriculture-Food and Environmental Sciences, Agricultural and Biosystems Engineering Research Unit, Università degli Studi di Perugia (UNIPG), Departamento de Geografía, Grup de Recerca Ambiental Mediterrània, University of Barcelona, Forest Science and Technology Centre of Catalonia, Department of Geography and Environmental Studies, University of Nairobi (UoN), Science and Technology Faculty, Hydro-Environmental Processes Research Group, University of the Basque Country (University of the Basque Country), Geographical Institute, Scientific Research Center of the Slovenian Academy of Sciences and Arts (ZRC SAZU), MINECO-FEDER [CGL2014-52135-C3-3-R, CGL2014-59946-R, CGL2015-65569-R, CGL2015-64284-C2-2-R, PCIN-2017-061/AEI], Spanish Ministry of Economy and Competitiveness, MEC [RYC-2013-14371, RYC-2010-06264], Spanish Ministry of Education, Culture and Sports, Portuguese Science and Technology Foundation [SFRH/BPD/120093/2016], Juan de la Cierva postdoctoral contract from the MEC [IJCI-2015-26463], Vicenc Mut postdoctoral fellowship from the Autonomous Balearic Government [CAIB PD/038/2016], Secretariat for Universities and Research of the Department of the Economy and Knowledge of the Autonomous Government of Catalonia [2014 SGR 645], CERCA Programme, COST action CONNECTEUR [ES1306], University of Zaragoza - Universidad de Zaragoza [Zaragoza], Instituto Pirenaico de Ecologìa = Pyrenean Institute of Ecology [Zaragoza] (IPE - CSIC), Consejo Superior de Investigaciones Científicas [Madrid] (CSIC), Institut National de Recherche en Génie Rural Eaux et Forêts (INRGREF), Ecole Nationale du Génie Rural, des Eaux et des Forêts (ENGREF)-Institution de la Recherche et de l'Enseignement Supérieur Agricoles [Tunis] (IRESA), Instituto Catalán de Investigación del Agua - ICRA (SPAIN) (ICRA), Universidad Pública de Navarra [Espagne] = Public University of Navarra (UPNA), Universidade de Aveiro, Universitat de València (UV), Université Cadi Ayyad [Marrakech] (UCA), Barcelona Supercomputing Center - Centro Nacional de Supercomputacion (BSC - CNS), Instituto de Agricultura Sostenible - Institute for Sustainable Agriculture (IAS CSIC), Universidad de Extremadura - University of Extremadura (UEX), Universidad de Málaga [Málaga] = University of Málaga [Málaga], Université Grenoble Alpes [2016-2019] (UGA [2016-2019]), Institut de Recherche pour le Développement (IRD)-Institut National de la Recherche Agronomique (INRA)-Centre international d'études supérieures en sciences agronomiques (Montpellier SupAgro)-Institut national d’études supérieures agronomiques de Montpellier (Montpellier SupAgro), University of Potsdam = Universität Potsdam, Eberhard Karls Universität Tübingen = Eberhard Karls University of Tuebingen, Universidad Autónoma de Madrid (UAM), Université Paul-Valéry - Montpellier 3 (UPVM), École Pratique des Hautes Études (EPHE), Université Paris sciences et lettres (PSL), Université Paul-Valéry - Montpellier 3 (UPVM)-Institut National de la Recherche Agronomique (INRA)-Centre international d'études supérieures en sciences agronomiques (Montpellier SupAgro)-École Pratique des Hautes Études (EPHE), Université Paris sciences et lettres (PSL)-Université Paris sciences et lettres (PSL)-Université de Montpellier (UM)-Centre National de la Recherche Scientifique (CNRS)-Institut de Recherche pour le Développement (IRD [France-Sud])-Institut national d’études supérieures agronomiques de Montpellier (Montpellier SupAgro), Ecologie fonctionnelle et biogéochimie des sols et des agro-écosystèmes (UMR Eco&Sols), Centre de Coopération Internationale en Recherche Agronomique pour le Développement (Cirad)-Institut de Recherche pour le Développement (IRD)-Institut National de la Recherche Agronomique (INRA)-Centre international d'études supérieures en sciences agronomiques (Montpellier SupAgro)-Institut national d’études supérieures agronomiques de Montpellier (Montpellier SupAgro), Université de Toulouse (UT)-Université de Toulouse (UT)-Institut national des sciences de l'Univers (INSU - CNRS)-Observatoire Midi-Pyrénées (OMP), Université de Toulouse (UT)-Université de Toulouse (UT)-Institut national des sciences de l'Univers (INSU - CNRS)-Centre National d'Études Spatiales [Toulouse] (CNES)-Centre National de la Recherche Scientifique (CNRS)-Météo-France -Institut national des sciences de l'Univers (INSU - CNRS)-Centre National d'Études Spatiales [Toulouse] (CNES)-Centre National de la Recherche Scientifique (CNRS)-Météo-France -Centre National de la Recherche Scientifique (CNRS)-Institut National de Recherche pour l’Agriculture, l’Alimentation et l’Environnement (INRAE), Université de Toulouse (UT), Universidad de Córdoba = University of Córdoba [Córdoba], Università degli Studi di Perugia = University of Perugia (UNIPG), Centre de Ciència i Tecnologia Forestal de Catalunya (CTFC), Pena-Angulo D., Nadal-Romero E., Gonzalez-Hidalgo J.C., Albaladejo J., Andreu V., Bagarello V., Barhi H., Batalla R.J., Bernal S., Bienes R., Campo J., Campo-Bescos M.A., Canatario-Duarte A., Canton Y., Casali J., Castillo V., Cerda A., Cheggour A., Cid P., Cortesi N., Desir G., Diaz-Pereira E., Espigares T., Estrany J., Fernandez-Raga M., Ferreira C.S.S., Ferro V., Gallart F., Gimenez R., Gimeno E., Gomez J.A., Gomez-Gutierrez A., Gomez-Macpherson H., Gonzalez-Pelayo O., Hueso-Gonzalez P., Kairis O., Karatzas G.P., Klotz S., Kosmas C., Lana-Renault N., Lasanta T., Latron J., Lazaro R., Le Bissonnais Y., Le Bouteiller C., Licciardello F., Lopez-Tarazon J.A., Lucia A., Marin C., Marques M.J., Martinez-Fernandez J., Martinez-Mena M., Martinez-Murillo J.F., Mateos L., Mathys N., Merino-Martin L., Moreno-de las Heras M., Moustakas N., Nicolau J.M., Novara A., Pampalone V., Raclot D., Rodriguez-Blanco M.L., Rodrigo-Comino J., Romero-Diaz A., Roose E., Rubio J.L., Ruiz-Sinoga J.D., Schnabel S., Senciales-Gonzalez J.M., Simonneaux V., Sole-Benet A., Taguas E.V., Taboada-Castro M.M., Taboada-Castro M.T., Todisco F., Ubeda X., Varouchakis E.A., Vericat D., Wittenberg L., Zabaleta A., Zorn M., Instituto Pirenaico de Ecologia (IPE), Institut national d'enseignement supérieur pour l'agriculture, l'alimentation et l'environnement (Institut Agro)-Institut national d'enseignement supérieur pour l'agriculture, l'alimentation et l'environnement (Institut Agro), Universidad Autonoma de Madrid (UAM), Centre National de la Recherche Scientifique (CNRS)-Université de Montpellier (UM)-Institut National de la Recherche Agronomique (INRA)-Centre de Coopération Internationale en Recherche Agronomique pour le Développement (Cirad)-Institut de Recherche pour le Développement (IRD [France-Sud]), Centre National de la Recherche Scientifique (CNRS)-Université de Montpellier (UM)-École pratique des hautes études (EPHE), Université Paris sciences et lettres (PSL)-Université Paris sciences et lettres (PSL)-Centre international d'études supérieures en sciences agronomiques (Montpellier SupAgro)-Institut National de la Recherche Agronomique (INRA)-Université Paul-Valéry - Montpellier 3 (UPVM)-Institut national d’études supérieures agronomiques de Montpellier (Montpellier SupAgro), Institut national d'enseignement supérieur pour l'agriculture, l'alimentation et l'environnement (Institut Agro)-Institut national d'enseignement supérieur pour l'agriculture, l'alimentation et l'environnement (Institut Agro)-Institut de Recherche pour le Développement (IRD [France-Sud]), Institut national d’études supérieures agronomiques de Montpellier (Montpellier SupAgro), Institut national d'enseignement supérieur pour l'agriculture, l'alimentation et l'environnement (Institut Agro)-Institut national d'enseignement supérieur pour l'agriculture, l'alimentation et l'environnement (Institut Agro)-Centre international d'études supérieures en sciences agronomiques (Montpellier SupAgro)-Centre de Coopération Internationale en Recherche Agronomique pour le Développement (Cirad)-Institut de Recherche pour le Développement (IRD)-Institut National de la Recherche Agronomique (INRA), Centre National de la Recherche Scientifique (CNRS)-Institut de Recherche pour le Développement (IRD)-Institut National de Recherche pour l’Agriculture, l’Alimentation et l’Environnement (INRAE)-Université Toulouse III - Paul Sabatier (UT3), Université Fédérale Toulouse Midi-Pyrénées-Université Fédérale Toulouse Midi-Pyrénées-Institut national des sciences de l'Univers (INSU - CNRS)-Observatoire Midi-Pyrénées (OMP), and Météo France-Centre National d'Études Spatiales [Toulouse] (CNES)-Université Fédérale Toulouse Midi-Pyrénées-Centre National de la Recherche Scientifique (CNRS)-Institut de Recherche pour le Développement (IRD)-Météo France-Centre National d'Études Spatiales [Toulouse] (CNES)-Centre National de la Recherche Scientifique (CNRS)
- Subjects
010504 meteorology & atmospheric sciences ,Runoff ,Erosion ,Mediterranean basin ,Sediment yield ,Synoptic weather types ,0207 environmental engineering ,[SDU.STU]Sciences of the Universe [physics]/Earth Sciences ,02 engineering and technology ,01 natural sciences ,Mediterranean Basin ,Hydrology (agriculture) ,Erosão, Produção de sedimentos, Escoamento, Bacia Mediterrânica ,Soil retrogression and degradation ,ddc:550 ,020701 environmental engineering ,0105 earth and related environmental sciences ,Water Science and Technology ,Hydrology ,Sediment ,Institut für Umweltwissenschaften und Geographie ,15. Life on land ,6. Clean water ,13. Climate action ,Environmental science ,Spatial variability ,Soil conservation ,Surface runoff - Abstract
Este artículo contiene 16 páginas, 6 figuras, 2 tablas., Soil degradation by water is a serious environmental problem worldwide, with specific climatic factors being the major causes. We investigated the relationships between synoptic atmospheric patterns (i.e. weather types, WTs) and runoff, erosion and sediment yield throughout the Mediterranean basin by analyzing a large database of natural rainfall events at 68 research sites in 9 countries. Principal Component Analysis (PCA) was used to identify spatial relationships of the different WTs including three hydro-sedimentary variables: rainfall, runoff, and sediment yield (SY, used to refer to both soil erosion measured at plot scale and sediment yield registered at catchment scale). The results indicated 4 spatial classes of rainfall and runoff: (a) northern sites dependent on North (N) and North West (NW) flows; (b) eastern sites dependent on E and NE flows; (c) southern sites dependent on S and SE flows; and, finally, (d) western sites dependent on W and SW flows. Conversely, three spatial classes are identified for SY characterized by: (a) N and NE flows in northern sites (b) E flows in eastern sites, and (c) Wand SW flows in western sites. Most of the rainfall, runoff and SY occurred during a small number of daily events, and just a few WTs accounted for large percentages of the total. Our results confirm that characterization by WT improves understanding of the general conditions under which runoff and SY occur, and provides useful information for understanding the spatial variability of runoff, and SY throughout the Mediterranean basin. The approach used here could be useful to aid of the design of regional water management and soil conservation measures., This research was supported by projects funded by the MINECOFEDER: CGL2014-52135-C3-3-R, CGL2014-59946-R, CGL2015-65569- R, CGL2015-64284-C2-2-R, and PCIN-2017-061/AEI. When this manuscript was first submitted Estela Nadal-Romero and Damià Vericat received a “Ramón y Cajal” postdoctoral contract (RYC-2013-14371 and RYC‐2010‐06264, Spanish Ministry of Economy and Competitiveness, MEC). Damià Vericat is now a Serra Húnter Fellow at the University of Lleida. María Fernández-Raga received a “José Castillejo” postdoctoral grant (Spanish Ministry of Education, Culture and Sports). Carla Ferreira was supported by a post-doctoral research grant from the Portuguese Science and Technology Foundation (SFRH/ BPD/120093/2016). Mariano Moreno-de las Heras received a Juan de la Cierva postdoctoral contract (IJCI-2015-26463) from the MEC. José Andrés López-Tarazón received a Vicenç Mut postdoctoral fellowship from the Autonomous Balearic Government (CAIB PD/038/2016). José Andrés López-Tarazón and Ramon Batalla also acknowledge the Secretariat for Universities and Research of the Department of the Economy and Knowledge of the Autonomous Government of Catalonia for supporting the Consolidated Research Group 2014 SGR 645 (RIUSFluvial Dynamics Research Group), and the CERCA Programme. This paper has benefited from the Lab and Field Data Pool created within the framework of the COST action CONNECTEUR (ES1306).
- Published
- 2019
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3. Shrub clearing and extensive livestock as a strategy for enhancing ecosystem services in degraded Mediterranean mid-mountain areas.
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Lasanta T, Cortijos-López M, Errea MP, Llena M, Sánchez-Navarrete P, Zabalza J, and Nadal-Romero E
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- Animals, Soil chemistry, Carbon, Livestock, Ecosystem, Fires
- Abstract
Land abandonment in the Mediterranean mountains since the 20th century has led to a reduction of ecosystem services, due to revegetation and homogenization of the landscape. To counteract these effects, the regional administration of La Rioja in Spain initiated a Plan for Shrub Clearing (PSC) combined with extensive livestock grazing in 1986, which is still in action today. This study analyses the effects of pairing clearing with grazing in an experimental area of the Leza valley (Iberian System) on: (i) the landscape structure and structural diversity; (ii) the production of pasture; (iii) fire control; (iv) soil organic carbon sequestration (also considering soil environmental types); (v) surface water resources. The results show that: (i) a more fragmented landscape with greater diversity is created; (ii) grazing land is almost doubled in alkaline soils and four-fold in siliceous soils; (iii) fires are considerably reduced, with the mean surface fire spread falling from 34.1 ha/year from 1968 to 1985, to 1.2 ha/year between 1986 and 2022; (iv) regenerated post-clearance grazing soils sequester more organic carbon than that of shrublands, especially older clearings on alkaline soils (55.3 % more); (v) clearing increases hydrological connectivity and water resources. The conclusion is that managing the Mediterranean mid-mountains could be a very effective strategy to improve the supply of certain ecosystem services and improve the current socio-economic perspective of these marginal areas in a context of Global Change. The PSC also contributes to local development by increasing livestock numbers., Competing Interests: Declaration of competing interest The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper., (Copyright © 2023 The Authors. Published by Elsevier B.V. All rights reserved.)
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- 2024
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4. Carbon sequestration and water yield tradeoffs following restoration of abandoned agricultural lands in Mediterranean mountains.
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Khorchani M, Nadal-Romero E, Lasanta T, and Tague C
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- Agriculture, Carbon analysis, Mediterranean Region, Water, Carbon Sequestration, Ecosystem
- Abstract
Abandoned cropland areas have the potential to contribute to climate change mitigation through natural revegetation and afforestation programs. These programs increase above and belowground carbon sequestration by expanding forest cover. However, this potential to mitigate climate change often involves tradeoffs between carbon sequestration and water availability. Particularly in a water limited environments such as the Mediterranean region, any loss of recharge to groundwater or streamflow can have critical societal consequences. In this study, we used an ecohydrologic model, Regional Hydro-Ecological Simulation System (RHESSys), to quantify these tradeoffs for land management plans in abandoned cropland areas in Mediterranean mountains. Changes to Net Ecosystem Production (NEP), water yield and Water-Use Efficiency (WUE) under different land management and climate scenarios were estimated for Arnás, a catchment with similar geology, vegetation and climate to many of the locations targeted for land abandonment restoration in the Spanish Pyrenees. Results showed significant changes to both carbon and water fluxes related to land management, while changes related to a warming scenario were not significant. Afforestation scenarios showed the highest average annual carbon sequestration rates (112 g C·m
-2 ·yr-1 ) but were also associated with the lowest water yield (runoff coefficient of 26%) and water use efficiency (1.4 g C·mm-1 ) compared to natural revegetation (-27 g C·m-2 ·yr-1 , 50%, 1.7 g C·mm-1 respectively). Under both restoration scenarios, results showed that the catchment ecosystem is a carbon sink during mid-February to July, coinciding with peak monthly transpiration and WUE, while during the rest of the year the catchment ecosystem is a carbon source. These results contribute to understanding carbon and water tradeoffs in Mediterranean mountains and can help adapt restoration plans to address both carbon sequestration and water management objectives., (Copyright © 2021 The Authors. Published by Elsevier Inc. All rights reserved.)- Published
- 2022
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5. 20-Years of hindsight into hydrological dynamics of a mountain forest catchment in the Central Spanish Pyrenees.
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Juez C, Peña-Angulo D, Khorchani M, Regüés D, and Nadal-Romero E
- Abstract
Mediterranean mountain forests play a significant role in hydrological regulation. In this study, hydrological dynamics was examined at different temporal scales in a small mountain forest catchment in the Central Spanish Pyrenees (San Salvador), based on a 20-year dataset (1999-2019). Mean annual runoff coefficient is 0.21, and ranged from 0.02 to 0.58. The catchment has a bi-modal hydrological behavior with two hydrological periods: a dry-period between July and December, and a wet-period between January and June. During the study period, only 108 floods were recorded, suggesting a low responsiveness of the catchment, with a high variable response. Spearman correlation analysis and stepwise multivariate regression suggest that the hydrological response in the San Salvador catchment is mainly depending on water table, with antecedent moisture conditions and rainfall depth as secondary factors. Seasonal differences were also observed: during dry season, the response was mainly related to rainfall depth and rainfall intensity; in contrast in wet season, the response was mainly related to antecedent conditions (previous rainfall and base flow). Thus, the already challenging water resources management in the Mediterranean basin is magnified by the key function of forests as natural modulators of water cycle. Consequently, the study of natural forested catchments is needed and long-datasets have to be analysed to understand the role of natural Mediterranean forest in the hydrological dynamics and its evolution and adaptation in a context of Global Change., Competing Interests: Declaration of competing interest The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper., (Copyright © 2020 Elsevier B.V. All rights reserved.)
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- 2021
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6. Influence of weather types on the hydrosedimentary response in three small catchments on the Island of Mallorca, Spain.
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Peña-Angulo D, Estrany J, García-Comendador J, Fortesa J, Tomàs-Burguera M, Company J, Alorda B, and Nadal-Romero E
- Subjects
- Floods, Islands, Spain, Water Movements, Hydrology, Weather
- Abstract
The influence of the sea and topography are vital factors in the atmospheric processes affecting any island, as they introduce peculiarities in the hydrosedimentary response of fluvial systems. In view of that, the relationship between the surface atmospheric conditions (weather types, WTs), rainfall, runoff and erosion dynamics in three small catchments located in Mallorca were analysed. The catchments are representative in terms of geomorphology and land use but also due to their location within the major rainfall areas previously identified in the island by (Sumner et al., 1993). Data of rainfall, runoff and sediment variables, coupled with calculated WTs were used for the 2013-2017 period. WTs frequency and distribution during this period were compared to the last climatic period reference (1981-2010) to test the climate validity of the study period. The results illustrated how hydrosedimentary response was mostly caused by eco-geographical patterns but also by differences in the response of each catchment to WTs, related to the intrinsic geographical position in the island and different exposures to humid winds. Anticyclonic WT was the most frequent, despite it being only involved in one flood event at the eastern catchment. Conversely, eastern and northeastern WTs generated more than 85% of the total runoff and sediment, representing only 39% of flood events. The understanding of the specific role of WTs on the island's hydrology was improved, considering that freshwater resources are scarce and eco-sociologically crucial., (Copyright © 2020 Elsevier Inc. All rights reserved.)
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- 2021
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7. Long-term time-scale bonds between discharge regime and catchment specific landscape traits in the Spanish Pyrenees.
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Juez C and Nadal-Romero E
- Subjects
- Hydrology, Plants, Rivers, Agriculture, Forests
- Abstract
An analysis of long-term databases with information on precipitation and discharge records was undertaken to characterize the temporal structure response of four experimental catchments, located in the Central Spanish Pyrenees, with a gradient of land-cover (from a relatively pristine forested catchment, through an abandoned cultivated catchment with progressive plant recolonization, to an afforested catchment and ending with a degraded badlands catchment). Precipitation and discharge records are non-stationary and the wavelet transform methodology was thus applied to perform a temporal scale-by-scale analysis of each catchment response to the hydroclimatic characteristics of the area. This temporal decomposition analysis illustrates how land-use and land-cover legacy control the temporal distribution of flow events occurring at different and non-similar time-scales, thus reflecting the timing, variability and physical mechanisms of water storage/transport in each catchment. Intra-annual and annual time-scales are led by climatological characteristics of the catchment sites (seasonal patterns of mountainous Pyrenees catchments). Multi-year scale is mainly shaped by land-cover and land-use legacy. Badlands catchment, with its large proportion of bare land, shows a discharge response closely synchronized with precipitation patterns for all time-scales. On the contrary, for the forested catchment the global hydrological response is mainly governed by the multi-year time-scale. Afforested catchment and abandoned cultivated catchment, which move towards a pristine forest response, are impacted by the former grazing and agriculture activities and intra-annual temporal variability still play a major role on the global discharge response of the catchment. This suggests that vegetated catchments located in the same region can show hydrological responses at different time-scales to the same climatic input. We argue that differences in land-cover and historical land-use changes are not only valuable to understand the current discharge temporal behaviour, but they will also play a significant role in characterizing the future catchment dynamics due to changing climate conditions., (Copyright © 2020 Elsevier Inc. All rights reserved.)
- Published
- 2020
- Full Text
- View/download PDF
8. Effects of active and passive land use management after cropland abandonment on water and vegetation dynamics in the Central Spanish Pyrenees.
- Author
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Khorchani M, Nadal-Romero E, Tague C, Lasanta T, Zabalza J, Lana-Renault N, Domínguez-Castro F, and Choate J
- Subjects
- Agriculture, Carbon, Soil, Spain, Water, Crops, Agricultural
- Abstract
The Mediterranean mountains have been subject to significant land abandonment process during the second half of the 20th century. The subsequent natural revegetation following abandonment in rural areas has been widely documented to have substantial implications on the hydrological cycle and the vegetation. The Spanish Pyrenees are one of the most affected areas by these land transformations which could threaten their importance for water supply and agricultural activities in the downstream lowland areas. Land managers as well as scientists around the world have taken different positions on how to deal with these land use changes. Some are in favor of active management (AM) (i.e. density reduction) while others are supporting passive management (PM) (letting the process of revegetation continue). This study aims to investigate the implication of AM and PM on hydrological and vegetation dynamics under different climate trajectories in a representative abandoned cropland catchment in the Central Spanish Pyrenees. A coupled ecohydrologic model is used to estimate the post management response of streamflow (STR), evapotranspiration (ET), soil saturation deficit (SD) and plant carbon (PC) following shrub clearing. Clearing increased annual STR by 16%, while ET and SD decreased by around -9% and -6% respectively during the first year after management with changes to monthly flows. These changes to water regimes may be even higher in wetter years. Over a 10-years period of vegetation recovery annual STR increased between 7.1% and 24.2%, while annual ET and SD decreased between -2.6% to -8.7% and -2.7% to -6% respectively due to shrub clearing, with the highest changes occurring in the first three years of AM. On the effect of climate change, our results show that a 2 °C increase in temperature could reduce AM effects on water regimes and accelerate the recovery of PC given averaged rainfall conditions., Competing Interests: Declaration of competing interest The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper., (Copyright © 2020 Elsevier B.V. All rights reserved.)
- Published
- 2020
- Full Text
- View/download PDF
9. Editorial: Soil processes in mountain environments.
- Author
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Nadal Romero E, Pereira P, and Martínez-Murillo JF
- Subjects
- Altitude, Animals, Ecosystem, Livestock, Agriculture, Climate Change, Forestry, Soil, Urbanization
- Published
- 2019
- Full Text
- View/download PDF
10. The enhancing effect of afforestation over secondary succession on soil quality under semiarid climate conditions.
- Author
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Zethof JHT, Cammeraat ELH, and Nadal-Romero E
- Abstract
Semiarid climate conditions hamper natural re-vegetation, leaving the soil vulnerable to erosion after the cessation of agriculture. Therefore, soil and landscape protective measures, especially afforestations, have been implemented in the Mediterranean region since the early 20th century. This study aims to determine the long term impact of afforestation on soil functioning, in comparison with natural re-vegetation (secondary succession) on abandoned fields and semi-natural vegetation. A comparison of secondary succession and afforestation with the present traditional rain fed cereal fields and semi-natural (open) forest, including natural resource islands, was made as well. Composite soil samples were taken to study the physical (i.e. texture, aggregate stability) and chemical (i.e. carbon content, nutrient availability) soil characteristics after 20 and 40 years of afforestation and secondary natural succession. To take into account the resource island effect, the spatial heterogeneity induced by differences in plant cover, samples were taken both below and in between the tree canopy of the semi-natural and afforested Pinus halepensis trees. Our results indicate that under secondary succession on abandoned fields, soil quality improves non-linearly and only marginally over a time of 40 years. The afforestation showed a much more pronounced linear increase for most soil quality indicators, resulting in soil conditions comparable to what can be found under the semi-natural forest vegetation. Site preparation might have been a crucial factor for the success of ecosystem restoration in the studied dry land area as it improved water availability for the afforestation., (Copyright © 2018 Elsevier B.V. All rights reserved.)
- Published
- 2019
- Full Text
- View/download PDF
11. Woody encroachment and soil carbon stocks in subalpine areas in the Central Spanish Pyrenees.
- Author
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Nadal-Romero E, Otal-Laín I, Lasanta T, Sánchez-Navarrete P, Errea P, and Cammeraat E
- Abstract
Woody encroachment has been an ongoing process in the subalpine belt of Mediterranean mountains, after land abandonment, the disappearance of the transhumant system and the decrease of the livestock number. The main objectives of this study were: (i) to identify land use/land cover (LULC) changes from 1956 to 2015, and (ii) to investigate the effects of LULC changes in physical and chemical soil properties and soil organic carbon (SOC) and nitrogen (N) stocks. It is hypothesized that woody encroachment in the subalpine belt may lead to significant changes in soil properties, and will generate an increase in the SOC stocks. A land use gradient was identified in the subalpine belt of the Central Spanish Pyrenees: (i) subalpine grasslands, (ii) shrublands, (iii) young forests, and (iv) old forests. Mineral soil samples were collected every 10 cm, down to 40 cm, at three points per each LULC and a total of 48 samples were analyzed. The results showed that (i) woody encroachment has occurred from 1956 to 2015 due to the expansion of coniferous forests and shrublands (at the expense of grasslands), (ii) land cover and soil depth had significant effects on soil properties (except for pH), being larger in the uppermost 0-10 cm depth, (iii) SOC and N contents and stocks were higher in the grassland sites, and (iv) the woody encroachment process initially produced a decrease in the SOC stocks (shrublands), but no differences were observed considering the complete soil profile between grasslands and young and old forests. Further studies, describing SOC stabilization and quantifying above-ground carbon (shrub and tree biomass) are required., (Copyright © 2018 Elsevier B.V. All rights reserved.)
- Published
- 2018
- Full Text
- View/download PDF
12. The footprint of marginal agriculture in the Mediterranean mountain landscape: An analysis of the Central Spanish Pyrenees.
- Author
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Lasanta T, Nadal-Romero E, and Errea MP
- Abstract
Agriculture forms an essential part of the mountains of the Mediterranean. For centuries, large areas were cultivated to feed the local population, with highly marginal slopes being tilled at times of heavy demographic pressure, using the shifting agriculture system. A great deal of agricultural land was abandoned during the 20th century, giving rise to secondary succession processes that tend to eliminate the agricultural footprint. However, revegetation is a highly complex process leading to areas with dense, well-structured plant cover, and other open areas of scrubland. This article studies the role of traditional agriculture in the deterioration of the landscape. By using experimental plots in the Central Pyrenees to reproduce traditional agriculture and abandonment, maps of field types, and current uses and ground cover, it could be confirmed that shifting agriculture has caused very heavy soil loss, which explains the deterioration of the landscape on several slopes. Burning scrub and adding the ash to the soil as a fertilizer did not greatly help to improve soil quality, but caused high rates of erosion and a very slow process of regrowth. The average data obtained from the shifting experimental plots recorded losses of 1356kgha
-1 years-1 , 1.6 times more than the plot of fertilized cereal, and 8.2 times more than the dense scrub plot. Following abandonment, losses in the shifting agriculture plot were almost three times higher than the abandoned sloping field plot. Traditional shifting agriculture in the Pyrenees is the main cause of the deterioration of the landscape 50-70years after agriculture ceased., (Copyright © 2017 Elsevier B.V. All rights reserved.)- Published
- 2017
- Full Text
- View/download PDF
13. How do soil organic carbon stocks change after cropland abandonment in Mediterranean humid mountain areas?
- Author
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Nadal-Romero E, Cammeraat E, Pérez-Cardiel E, and Lasanta T
- Abstract
The effects of land use changes on soil carbon stocks are a matter of concern stated in international policy agendas on the mitigation of greenhouse emissions. Afforestation is increasingly viewed as an environmental restorative land use change prescription and is considered one of the most efficient carbon sequestration strategies currently available. Given the large quantity of CO2 that soils release annually, it is important to understand disturbances in vegetation and soil resulting from land use changes. The main objective of this study is to assess the effects of land abandonment, land use change and afforestation practices on soil organic carbon (SOC) dynamics. For this aim, five different land covers (bare soil, permanent pastureland, secondary succession, Pinus sylvestris (PS) and Pinus nigra (PN) afforestation), in the Central Spanish Pyrenees, were analysed. SOC dynamics have been studied in the bulk soil, and in the fractions separated according to two methodologies: (i) aggregate size distribution, and (ii) density fractionation, and rates of carbon mineralization have been determined by measuring CO2 evolution using an automated respirometer. The results showed that: (i) SOC contents were higher in the PN sites in the topsoil (10cm), (ii) when all the profiles were considered no significant differences were observed between pastureland and PN, (iii) SOC accumulation under secondary succession is a slow process, and (iv) pastureland should also be considered due to the relative importance in SOC stocks. The first step of SOC stabilization after afforestation is the formation of macro-aggregates promoted by large inputs of SOC, with a high contribution of labile organic matter. However, our respiration experiments did not show evidence of SOC stabilization. SOC mineralization was higher in the top layers and values decreased with depth. These results gain insights into which type of land management is most appropriate after land abandonment for SOC., (Copyright © 2016 Elsevier B.V. All rights reserved.)
- Published
- 2016
- Full Text
- View/download PDF
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