Evaluating the effect of satellite image resolution for predictive habitat mapping: a sensitivity analysis in the Cantabrian Mountains (NW Spain)

Authors and Affiliations: 

Jose Manuel Álvarez-Martínez 1, Borja Jiménez-Alfaro 2, Ana Silió-Calzada 1, David López 3, Aurelio Martí 4 and José Barquín 1

1 Environmental Hydraulics Institute IH Cantabria, C/ Isabel Torres nº 15, Parque Científico y Tecnológico de Cantabria 39011, Santander, Spain.

2 Department of Botany and Zoology, Masaryk University, Kotlarska 2, CZ-61137
Brno, Czech Republic

3 ITD Medio Ambiente. Edificio 3000 (Módulo 12). Parque Científico y Tecnológico
de Cantabria (PCTCAN). 39011 Santander

4 DEIMOS IMAGING, an UrtheCast Company. Ronda de Poniente 19, 28760 Tres Cantos (Madrid), Spain

Corresponding author: 
Jose Manuel Álvarez-Martínez
Abstract: 

A current biodiversity conservation challenge is to estimate the spatial extent of habitat types as defined by the guidelines of environmental policies such as the Habitats Directive (92/43/EEC) and moving beyond landscape patterns of broader vegetation types. In the absence of field-based fine-resolution maps (Evans 2006; Vanden Borre et al. 2011), predictive models based on environmental variables can represent a valuable tool, helping the assessment of the local area of occurrence (AOO) of vegetation communities (Figure 1) (Ferrier & Guisan 2006; Elith, Kearney & Phillips 2010; Rodríguez et al. 2015). However, the implementation of these tools is still uncommon in regional conservation planning (Wiens et al, 2009). Among other factors, vegetation mapping is hampered by the complexity of natural systems due to environmental or successional gradients, plant traits and human disturbances acting altogether at different spatial and temporal scales (Álvarez-Martínez et al. 2014). Recent developments in data availability and processing methods have linked this monitoring task to remote sensing (RS) (Nagendra et al. 2013; Corbane et al. 2015). Satellite imagery temporal, spectral and spatial resolutions allow the exploration of different vegetation status and phenology aspects, which may lead to a proper habitat type discrimination (Lillesand et al., 2008). In this study, we combined data obtained from different sources: i) an intensive vegetation survey across a Special Area of Conservation of the Cantabria region (Spain), dominated by peatlands, bogs, grasslands and heathlands, ii) abiotic limiting factors (i.e. topography, climate and soil properties), iii) LiDAR data informing about vegetation height and structure, and iv) three different satellite images (Figure 2). In order to study the role played by satellite data resolutions, we first chose two Landsat8 OLI images (30-m pixel size) collected during the spring and summer of 2016, to evaluate the predictive skills of temporal resolution. Secondly, we used a Sentinel-2 MSI image from summer 2016, in order to assess the combined effect of a 10-m pixel size and enhanced near infrared spectral capabilities. Lastly, we analyzed a Deimos-2 image, with a pixel size of 3.3 meters. A Landsat summer image was used to generate baseline models, to be compared to the former three approaches. All maps were validated at different levels. We calculated ommision-commission errors and overall accuracy scores by using independent field checked points for the habitat types encountered across the study area. Subsequently, we determined how each modelling aproach (i.e. using temporally, spectrally and spatially enhanced satellite imagery) differed from the baseline approach of a single Landsat image. The results of this study represent and important step towards improving, in complex landscapes, the identification of habitat type occupancy areas under current Global Change effects.

References: 

Álvarez-Martínez, J.M., Suárez-Seoane, S., Stoorvogel, J.J. & de Luis Calabuig, E. (2014) Influence of land use and climate on recent forest expansion: a case study in the Eurosiberian–Mediterranean limit of north-west Spain. Journal of Ecology, 102, 905-919.

Corbane, C., Lang, S., Pipkins, K., Alleaume, S., Deshayes, M., García Millán, V.E., Strasser, T., Vanden Borre, J., Toon, S. & Michael, F. (2015) Remote sensing for mapping natural habitats and their conservation status – New opportunities and challenges. International Journal of Applied Earth Observation and Geoinformation, 37, 7-16.

Elith, J., Kearney, M. & Phillips, S. (2010) The art of modelling range-shifting species. Methods in Ecology and Evolution, 1, 330-342.

Evans, D. (2006) The Habitats of the European Union Habitats Directive. Biology & Environment: Proceedings of the Royal Irish Academy, 106, 167-173.

Ferrier, S. & Guisan, A. (2006) Spatial modelling of biodiversity at the community level. Journal of Applied Ecology, 43, 393-404.

Lillesand, Thomas M. , Ralph W. Kiefer, and Jonathan W. Chipman. 2008. Remote Sensing and Image Interpretation: John Wiley & Sons

Nagendra, H., Lucas, R., Honrado, J.P., Jongman, R.H.G., Tarantino, C., Adamo, M. & Mairota, P. (2013) Remote sensing for conservation monitoring: Assessing protected areas, habitat extent, habitat condition, species diversity, and threats. Ecological Indicators, 33, 45-59.

Rodríguez, J.P., Keith, D.A., Rodríguez-Clark, K.M., Murray, N.J., Nicholson, E., Regan, T.J., Miller, R.M., Barrow, E.G., Bland, L.M. & Boe, K. (2015) A practical guide to the application of the IUCN Red List of Ecosystems criteria. Phil. Trans. R. Soc. B, 370, 20140003.

Vanden Borre, J., Paelinckx, D., Mücher, C.A., Kooistra, L., Haest, B., De Blust, G. & Schmidt, A.M. (2011) Integrating remote sensing in Natura 2000 habitat monitoring: Prospects on the way forward. Journal for Nature Conservation, 19, 116-125.

Wiens, John, Robert Sutter, Mark Anderson, Jon Blanchard, Analie Barnett, Naikoa Aguilar-Amuchastegui, Chadwick Avery, and Stephen Laine. 2009. "Selecting and conserving lands for biodiversity: The role of remote sensing." Remote Sensing of Environment 113 (7):1370-81.

Oral or poster: 
Oral presentation
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