Isabel Afán

Isabel Afán

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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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3 February 2017 in Science Advances
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FRFrancisco Ramírez
Francisco Ramírez
IAIsabel Afán
Isabel Afán
LDLloyd S. Davis
Lloyd S. Davis
ACAndré Chiaradia
André Chiaradia
The main hot spots of marine biodiversity are also the areas that are affected the most by climate and, potentially, fishing impacts.

4 March 2013 in Ecography
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Journal Article
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AFAlbert Fernández‐Chacón
Albert Fernández‐Chacón
MGMeritxell Genovart
Meritxell Genovart
RPRoger Pradel
Roger Pradel
GTGiacomo Tavecchia
Giacomo Tavecchia
ABAlbert Bertolero
Albert Bertolero
DODaniel Oro
Daniel Oro

31 August 2017 in Marine Ecology Progress Series
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Journal Article
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JNJoan Navarro
Joan Navarro
DGDavid Grémillet
David Grémillet
FRFrancisco J. Ramirez
Francisco J. Ramirez
IAIsabel Afán
Isabel Afán
WBWillem Bouten
Willem Bouten
MFManuela G. Forero
Manuela G. Forero

19 December 2013 in Marine Biology
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IAIsabel Afán
Isabel Afán
JNJoan Navarro
Joan Navarro
LCLaura Cardador
Laura Cardador
FRFrancisco Ramírez
Francisco Ramírez
AKAkiko Kato
Akiko Kato
MFManuela G. Forero
Manuela G. Forero

20 September 2016 in Remote Sensing
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Journal Article
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Ricardo Díaz-DelgadoRicardo Díaz-Delgado
Ricardo Díaz-Delgado
DADavid Aragones
David Aragones
IAIsabel Afán
Isabel Afán
Javier BustamanteJavier Bustamante
Javier Bustamante
This paper presents a semi-automatic procedure to discriminate seasonally flooded areas in the shallow temporary marshes of Doñana National Park (SW Spain) by using a radiommetrically normalized long time series of Landsat MSS, TM, and ETM+ images (1974–2014). Extensive field campaigns for ground truth data retrieval were carried out simultaneous to Landsat overpasses. Ground truth was used as training and testing areas to check the performance of the method. Simple thresholds on TM and ETM band 5 (1.55–1.75 μm) worked significantly better than other empirical modeling techniques and supervised classification methods to delineate flooded areas at Doñana marshes. A classification tree was applied to band 5 reflectance values to classify flooded versus non-flooded pixels for every scene. Inter-scene cross-validation identified the most accurate threshold on band 5 reflectance (ρ < 0.186) to classify flooded areas (Kappa = 0.65). A joint TM-MSS acquisition was used to find the MSS band 4 (0.8 a 1.1 μm) threshold. The TM flooded area was identical to the results from MSS 4 band threshold ρ < 0.10 despite spectral and spatial resolution differences. Band slicing was retrospectively applied to the complete time series of MSS and TM images. About 391 flood masks were used to reconstruct historical spatial and temporal patterns of Doñana marshes flooding, including hydroperiod. Hydroperiod historical trends were used as a baseline to understand Doñana’s flooding regime, test hydrodynamic models, and give an assessment of relevant management and restoration decisions. The historical trends in the hydroperiod of Doñana marshes show two opposite spatial patterns. While the north-western part of the marsh is increasing its hydroperiod, the southwestern part shows a steady decline. Anomalies in each flooding cycle allowed us to assess recent management decisions and monitor their hydrological effects.

24 September 2013 in Journal of the Marine Biological Association of the United Kingdom
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Journal Article
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RERuth Esteban
Ruth Esteban
PVPhilippe Verborgh
Philippe Verborgh
PGPauline Gauffier
Pauline Gauffier
JGJoan Giménez
Joan Giménez
IAIsabel Afán
Isabel Afán
RSRenaud de Stephanis
Renaud de Stephanis
Killer whales have been described in the Gulf of Cadiz, southern Spain, in spring and in the Strait of Gibraltar in summer. A total of 11,276 cetaceans sightings coming from different sources (dedicated research surveys, whale watching companies and opportunistic observations) were used to create two presence–‘pseudo-absence’ predictive generalized additive models (GAM), where presence data were defined as sightings of killer whales and ‘pseudo-absence’ data as sightings of other cetacean species. One model was created using spring data when killer whales’ main prey, Atlantic bluefin tuna, enter the Mediterranean Sea, and the other model used summer data when Atlantic bluefin tuna return to the Atlantic Ocean. Both model predictions show that killer whales are highly associated with a probable distribution of bluefin tuna during their migration throughout the study area, constraining their distribution to the Gulf of Cadiz in spring and the Strait of Gibraltar in spring and summer. Knowledge of the distribution of killer whales in the study area is essential to establish conservation measures for this population.