Estela Romero

Dr. Estela Romero

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Research Focus & Metrics

Academic Career Length

17Years (2010-Present)

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

Representative Publications

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1 April 2016 in Environmental Science & Policy
Verified
Journal Article
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EREstela Romero
Estela Romero
RGRomain Le Gendre
Romain Le Gendre
JGJosette Garnier
Josette Garnier
GBGilles Billen
Gilles Billen
CFCédric Fisson
Cédric Fisson
PRPhilippe Riou
Philippe Riou

4 January 2012 in Biogeosciences
Verified
Journal Article
Open access
LLL. Lassaletta
L. Lassaletta
EREstela Romero
Estela Romero
GBG. Billen
G. Billen
JGJ. Garnier
J. Garnier
HGH. García-Gómez
H. García-Gómez
JRJ. V. Rovira
J. V. Rovira
Despite the particular management practices and climate characteristics of the Mediterranean regions, the literature dealing with N budgets in large catchments subjected to Mediterranean conditions is scarce. The present study aims to deepen our knowledge on the N cycle within the Ebro River Basin (NE Spain) by means of two different approaches: (1) calculating a global N budget in the Ebro River Basin and (2) calculating a series of detailed regional budgets at higher geographical resolution. N inputs and outputs were spatialized by creating a map based on the most detailed information available. Fluvial and atmospheric N export was estimated together with N retention. The Ebro River Basin annually receives a relatively high amount of new N (5118 kg N km−2 yr−1), mostly in the form of synthetic fertilizers (50%). Although it is a highly productive catchment, the net N input as food and feed import is also high (33%). Only 8% of this N is finally exported to the delta zone. Several territorial units characterized by different predominant uses (rainfed agriculture, irrigated agriculture and pastures) have differentiated N dynamics. However, due to the high density of irrigation channels and reservoirs that characterize Mediterranean catchments, N retention is very high in all of them (median value, 91%). These results indicate that problems of eutrophication due to N delivery in the coastal area may not be too severe but that high N retention values may instead lead to problems within the catchment, such as pollution of aquifers and rivers, as well as high atmospheric emissions. The most promising management measures are those devoted to reducing agricultural surpluses through a better balanced N fertilization.

1 October 2013 in Regional Environmental Change
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Journal Article
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LLLuis Lassaletta
Luis Lassaletta
GBGilles Billen
Gilles Billen
EREstela Romero
Estela Romero
JGJosette Garnier
Josette Garnier
Eduardo AguileraEduardo Aguilera
Eduardo Aguilera

30 January 2010 in Journal of Plankton Research
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Journal Article
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ILItziar Lekunberri
Itziar Lekunberri
TLThomas Lefort
Thomas Lefort
EREstela Romero
Estela Romero
EVEvaristo Vázquez-Domínguez
Evaristo Vázquez-Domínguez
CRCristina Romera-Castillo
Cristina Romera-Castillo
JGJosep Gasol
Josep Gasol
The Mediterranean coast receives large inputs of dust with a potential fertilization effect. We evaluated the effect of a wet dust deposition event on microbial abundance and activity, community structure and metabolic balance. Dust collected during a dust storm event was added to a series of microcosms. We added a realistic concentration (0.05 g L−1) based on the phosphorus concentration contained in the dust and, in addition, we included a P amended tank to distinguish the effect of dust from that of the phosphorus in the dust. We also included a higher dust concentration tank (0.5 g L−1). Dust increased the initial water–phosphorus concentration by 0.3 µM and the dissolved organic carbon (DOC) concentration by 14 µM, and increased bacterial abundance (1.8-fold) and bacterial production (5-fold). At the end of the experiment, primary production and community respiration were stimulated by dust and by P, but the net result of the addition of low amounts of dust was an initial switch towards heterotrophy, whereas the net result of the high-dust (DH) additions and the P addition was a shift towards autotrophy. Bacterial community structure changed little between P and low dust, but these were very different from the control and the DH communities.

30 July 2015 in Global Biogeochemical Cycles
Verified
Journal Article
Open access
PDF file
JGJosette Garnier
Josette Garnier
LLLuis Lassaletta
Luis Lassaletta
GBGilles Billen
Gilles Billen
EREstela Romero
Estela Romero
BGBruna Grizzetti
Bruna Grizzetti
JDJean‐Marcel Dorioz
Jean‐Marcel Dorioz
Phosphorus (P) plays a strategic role in agricultural production as well as in the occurrence of freshwater and marine eutrophication episodes throughout the world. Moreover, the scarcity and uneven distribution of minable P resources is raising concerns about the sustainability of long‐term exploitation. In this paper we analyze the P cycle in anthropic systems with an original multiscale approach (world region, country, and large basin scales) in two contrasting world regions representative of different trajectories in socioeconomic development for the 1961–2009 period: Europe (EU‐27)/France and the Seine River Basin, and Asia (ASEAN‐8)/Vietnam and the Red River Basin. Our approach highlights different trends in the agricultural and food production systems of the two regions. Whereas crop production increased until the 1980s in Europe and France and has stabilized thereafter, in ASEAN‐8 and Vietnam it began to increase in the 1980s and it is still rising today. These trends are related to the increasing use of fertilizers, although in European countries the amount of fertilizers sharply decreased after the 1980s. On average, the total P delivered from rivers to the sea is 3 times higher for ASEAN‐8 (300 kg P km−2 yr−1) than for EU‐27 countries (100 kg P km−2 yr−1) and is twice as high in the Red River (200 kg P km−2 yr−1) than in the Seine River (110 kg P km−2 yr−1), with agricultural losses to water in ASEAN‐8 3 times higher than in EU‐27. Based on the P flux budgets, this study discusses early warnings and management options according to the particularities of the two world regions, newly integrating the perspective of surface water quality with agricultural issues (fertilizers, crop production, and surplus), food/feed exchanges, and diet, defining the so‐called water‐agro‐food system.