Eduardo Aguilera

Dr. Eduardo Aguilera

Universidad Politécnica de Madrid, 28040 Madrid, Spain
orcid

Research Focus & Metrics

Academic Career Length

14Years (2013-Present)

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

Representative Publications

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1 March 2013 in Agriculture, Ecosystems & Environment
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Journal Article
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Eduardo AguileraEduardo Aguilera
Eduardo Aguilera
LLLuis Lassaletta
Luis Lassaletta
AGAndreas Gattinger
Andreas Gattinger
BGBenjamín S. Gimeno
Benjamín S. Gimeno

1 January 2013 in Agriculture, Ecosystems & Environment
Verified
Journal Article
Open access
Eduardo AguileraEduardo Aguilera
Eduardo Aguilera
LLLuis Lassaletta
Luis Lassaletta
Alberto Sanz CobeñaAlberto Sanz Cobeña
Alberto Sanz Cobeña
JGJosette Garnier
Josette Garnier
AVAntonio Vallejo
Antonio Vallejo
International audienceEnvironmental problems related to the use of synthetic fertilizers and to organic waste management have led to increased interest in the use of organic materials as an alternative source of nutrients for crops, but this is also associated with N2O emissions. There has been an increasing amount of research into the effects of using different types of fertilization on N2O emissions under Mediterranean climatic conditions, but the findings have sometimes been rather contradictory. Available information also suggests that water management could exert a high influence on N2O emissions. In this context, we have reviewed the current scientific knowledge, including an analysis of the effect of fertilizer type and water management on direct N2O emissions. A meta-analysis of compliant reviewed experiments revealed significantly lower N2O emissions for organic as opposed to synthetic fertilizers (23% reduction). When organic materials were segregated in solid and liquid, only solid organic fertilizer emissions were significantly lower than those of synthetic fertilizers (28% reduction in cumulative emissions). The EF is similar to the IPCC factor in conventionally irrigated systems (0.98% N2O-N N applied(-1)), but one order of magnitude lower in rainfed systems (0.08%). Drip irrigation produces intermediate emission levels (0.66%). Differences are driven by Mediterranean agro-climatic characteristics, which include low soil organic matter (SOM) content and a distinctive rainfall and temperature pattern. Interactions between environmental and management factors and the microbial processes involved in N2O emissions are discussed in detail. Indirect emissions have not been fully accounted for, but when organic fertilizers are applied at similar N rates to synthetic fertilizers, they generally make smaller contributions to the leached NO3- pool. The most promising practices for reducing N2O through organic fertilization include: (i) minimizing water applications; (ii) minimizing bare soil; (iii) improving waste management; and (iv) tightening N cycling through N immobilization. The mitigation potential may be limited by: (i) residual effect; (ii) the long-term effects of fertilizers on SOM; (iii) lower yield-scaled performance; and (iv) total N availability from organic sources. Knowledge gaps identified in the review included: (i) insufficient sampling periods; (ii) high background emissions; (iii) the need to provide N2O EF and yield-scaled EF; (iv) the need for more research on specific cropping systems; and (v) the need for full GHG balances. In conclusion, the available information suggests a potential of organic fertilizers and water-saving practices to mitigate N2O emissions under Mediterranean climatic conditions, although further research is needed before it can be regarded as fully proven, understood and developed. (C) 2012 Elsevier B.V. All rights reserved

15 May 2020 in Global Change Biology
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Journal Article
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Alicia LedoAlicia Ledo
Alicia Ledo
PSPete Smith
Pete Smith
AZAyalsew Zerihun
Ayalsew Zerihun
JWJeanette Whitaker
Jeanette Whitaker
Jose Luis Vicente-VicenteJose Luis Vicente-Vicente
Jose Luis Vicente-Vicente
JHJon Hillier
Jon Hillier
This study evaluates the dynamics of soil organic carbon (SOC) under perennial crops across the globe. It quantifies the effect of change from annual to perennial crops and the subsequent temporal changes in SOC stocks during the perennial crop cycle. It also presents an empirical model to estimate changes in the SOC content under crops as a function of time, land use, and site characteristics. We used a harmonized global dataset containing paired‐comparison empirical values of SOC and different types of perennial crops (perennial grasses, palms, and woody plants) with different end uses: bioenergy, food, other bio‐products, and short rotation coppice. Salient outcomes include: a 20‐year period encompassing a change from annual to perennial crops led to an average 20% increase in SOC at 0–30 cm (6.0 ± 4.6 Mg/ha gain) and a total 10% increase over the 0–100 cm soil profile (5.7 ± 10.9 Mg/ha). A change from natural pasture to perennial crop decreased SOC stocks by 1% over 0–30 cm (−2.5 ± 4.2 Mg/ha) and 10% over 0–100 cm (−13.6 ± 8.9 Mg/ha). The effect of a land use change from forest to perennial crops did not show significant impacts, probably due to the limited number of plots; but the data indicated that while a 2% increase in SOC was observed at 0–30 cm (16.81 ± 55.1 Mg/ha), a decrease in 24% was observed at 30–100 cm (−40.1 ± 16.8 Mg/ha). Perennial crops generally accumulate SOC through time, especially woody crops; and temperature was the main driver explaining differences in SOC dynamics, followed by crop age, soil bulk density, clay content, and depth. We present empirical evidence showing that the FAO perennialization strategy is reasonable, underscoring the role of perennial crops as a useful component of climate change mitigation strategies.

1 February 2017 in Agriculture, Ecosystems & Environment
Verified
Journal Article
Open access
Alberto Sanz CobeñaAlberto Sanz Cobeña
Alberto Sanz Cobeña
LLL. Lassaletta
L. Lassaletta
Eduardo AguileraEduardo Aguilera
Eduardo Aguilera
APA. del Prado
A. del Prado
JGJ. Garnier
J. Garnier
PSPete Smith
Pete Smith
Acknowledgements The authors would like to thank the Spanish National R+D+i Plan (AGL2012-37815-C05-01, AGL2012-37815-C05-04) and very specifically the workshop held in December 2016 in Butrón (Bizkaia) to synthesize the most promising measures to reduce N2O emissions from Spanish agricultural soils. BC3 is sponsored by the Basque Government. M. L. Cayuela thanks Fundación Seneca for financing the project 19281/PI/14. This paper has been produced within the context of the REMEDIA network: http://redremedia.wordpress.com/.Peer reviewedPostprintPostprin

1 February 2017 in Agriculture, Ecosystems & Environment
Verified
Journal Article
Closed access
MCMaria L. Cayuela
Maria L. Cayuela
Eduardo AguileraEduardo Aguilera
Eduardo Aguilera
Alberto Sanz CobeñaAlberto Sanz Cobeña
Alberto Sanz Cobeña
DADean C. Adams
Dean C. Adams
DADiego Abalos
Diego Abalos
LLLuis Lassaletta
Luis Lassaletta

1 May 2020 in Agricultural Systems
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Journal Article
Closed access
Eduardo AguileraEduardo Aguilera
Eduardo Aguilera
CDCipriano Díaz-Gaona
Cipriano Díaz-Gaona
RGRaquel García-Laureano
Raquel García-Laureano
CRCarolina Reyes-Palomo
Carolina Reyes-Palomo
GGGloria I. Guzmán
Gloria I. Guzmán
Vicente Rodriguez-EstevezVicente Rodriguez-Estevez
Vicente Rodriguez-Estevez