Alejandro Valdecantos

Dr. Alejandro Valdecantos

Forest Restoration, Centro de Estudios Ambientales del Mediterráneo | CEAM, Paterna, Spain
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Research Focus & Metrics

Academic Career Length

23Years (2004-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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1 March 2004 in Plant Ecology
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Journal Article
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JPJuli G. Pausas
Juli G. Pausas
CBCarme Bladé
Carme Bladé
AVAlejandro Valdecantos
Alejandro Valdecantos
JSJosé P. Seva
José P. Seva
DFDavid Fuentes
David Fuentes
RVRamon Vallejo
Ramon Vallejo

1 July 2018 in Science of The Total Environment
Verified
Journal Article
Closed access
IDIka Djukic
Ika Djukic
SKSebastian Kepfer-Rojas
Sebastian Kepfer-Rojas
ISInger Kappel Schmidt
Inger Kappel Schmidt
KLKlaus Steenberg Larsen
Klaus Steenberg Larsen
CBClaus Beier
Claus Beier
ZTZsolt Tóth
Zsolt Tóth

8 January 2024 in Proceedings of the National Academy of Sciences
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Journal Article
Open access
MSMelinda D. Smith
Melinda D. Smith
KWKate D. Wilkins
Kate D. Wilkins
MHMartin Holdrege
Martin Holdrege
PWPeter Wilfahrt
Peter Wilfahrt
SCScott L. Collins
Scott L. Collins
XZXiaoan Zuo
Xiaoan Zuo
Climate change is increasing the frequency and severity of short-term (~1 y) drought events—the most common duration of drought—globally. Yet the impact of this intensification of drought on ecosystem functioning remains poorly resolved. This is due in part to the widely disparate approaches ecologists have employed to study drought, variation in the severity and duration of drought studied, and differences among ecosystems in vegetation, edaphic and climatic attributes that can mediate drought impacts. To overcome these problems and better identify the factors that modulate drought responses, we used a coordinated distributed experiment to quantify the impact of short-term drought on grassland and shrubland ecosystems. With a standardized approach, we imposed ~a single year of drought at 100 sites on six continents. Here we show that loss of a foundational ecosystem function—aboveground net primary production (ANPP)—was 60% greater at sites that experienced statistically extreme drought (1-in-100-y event) vs. those sites where drought was nominal (historically more common) in magnitude (35% vs. 21%, respectively). This reduction in a key carbon cycle process with a single year of extreme drought greatly exceeds previously reported losses for grasslands and shrublands. Our global experiment also revealed high variability in drought response but that relative reductions in ANPP were greater in drier ecosystems and those with fewer plant species. Overall, our results demonstrate with unprecedented rigor that the global impacts of projected increases in drought severity have been significantly underestimated and that drier and less diverse sites are likely to be most vulnerable to extreme drought.

20 April 2012 in New Forests
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RVRamon Vallejo
Ramon Vallejo
ASAthanasios Smanis
Athanasios Smanis
ECEsteban Chirino
Esteban Chirino
DFDavid Fuentes
David Fuentes
AVAlejandro Valdecantos
Alejandro Valdecantos
Alberto VilagrosaAlberto Vilagrosa
Alberto Vilagrosa
Reforestation efforts in dryland ecosystems frequently encounter drought and limited soil productivity, although both factors usually interact synergistically to worsen water stress for outplanted seedlings. Land degradation in drylands (e.g. desertification) usually reduces soil productivity and, especially, soil water availability. In dry sub-humid regions, forest fires constitute a major disturbance affecting ecosystem dynamics and reforestation planning. Climate change projections indicate an increase of drought and more severe fire regime in many dryland regions of the world. In this context, the main target of plantation technology development is to overcome transplant shock and likely adverse periods, and in drylands this is mostly related to water limitations. In this paper, we discuss some selected steps that we consider critical for improving success in outplanting woody plants, both under current and projected climate change conditions including: (1) Plant species selection, (2) Improved nursery techniques, and (3) Improved planting techniques. The number of plant species used in reforestation is increasing rapidly, moving from a reduced set of well-known, easy-to-grow, widely used species, to a large variety of promising native species. Available technologies allow for reintroducing native plants and recovering critical ecosystem functions for many degraded drylands. However, climate change projections introduce large uncertainties about the sustainability of current reforestation practices. To cope with these uncertainties, adaptive restoration approaches are suggested, on the basis of improved plant quality, improved techniques for optimizing rain use efficiency in plantations, and exploring native plant species, including provenances and genotypes, for their resilience to fire and water use efficiency.

10 March 2016 in Solid Earth
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Edoardo Antonio Costantino. CostantiniEdoardo Antonio Costantino. Costantini
Edoardo Antonio Costantino. Costantini
Cristina BranquinhoCristina Branquinho
Cristina Branquinho
ANAlice Nunes
Alice Nunes
GSGudrun Schwilch
Gudrun Schwilch
ISIlan Stavi
Ilan Stavi
CZClaudio Zucca
Claudio Zucca
Soil indicators may be used for assessing both land suitability for restoration and the effectiveness of restoration strategies in restoring ecosystem functioning and services. In this review paper, several soil indicators, which can be used to assess the effectiveness of ecological restoration strategies in dryland ecosystems at different spatial and temporal scales, are discussed. The selected indicators represent the different viewpoints of pedology, ecology, hydrology, and land management. Two overall outcomes stem from the review. (i) The success of restoration projects relies on a proper understanding of their ecology, namely the relationships between soil, plants, hydrology, climate, and land management at different scales, which are particularly complex due to the heterogeneous pattern of ecosystems functioning in drylands. (ii) The selection of the most suitable soil indicators follows a clear identification of the different and sometimes competing ecosystem services that the project is aimed at restoring.

12 October 2019 in New Phytologist
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Journal Article
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MBMara Baudena
Mara Baudena
VSVictor M. Santana
Victor M. Santana
MBM.Jaime Baeza
M.Jaime Baeza
SBSusana Bautista
Susana Bautista
MEMaarten B. Eppinga
Maarten B. Eppinga
MRMax Rietkerk
Max Rietkerk
Summary: Recent observations suggest that repeated fires could drive Mediterranean forests to shrublands, hosting flammable vegetation that regrows quickly after fire. This feedback supposedly favours shrubland persistence and may be strengthened in the future by predicted increased aridity. An assessment was made of how fires and aridity in combination modulated the dynamics of Mediterranean ecosystems and whether the feedback could be strong enough to maintain shrubland as an alternative stable state to forest. A model was developed for vegetation dynamics, including stochastic fires and different plant fire‐responses. Parameters were calibrated using observational data from a period up to 100 yr ago, from 77 sites with and without fires in Southeast Spain and Southern France. The forest state was resilient to the separate impact of fires and increased aridity. However, water stress could convert forests into open shrublands by hampering post‐fire recovery, with a possible tipping point at intermediate aridity. Projected increases in aridity may reduce the resilience of Mediterranean forests against fires and drive post‐fire ecosystem dynamics toward open shrubland. The main effect of increased aridity is the limitation of post‐fire recovery. Including plant fire‐responses is thus fundamental when modelling the fate of Mediterranean‐type vegetation under climate‐change scenarios.