UNCORRECTED PROOF
AMRE [1.30] 2006/11/21 11:19; Prn:7/01/2009; 10:47 F:amre2600.tex; VTeX/Milda p. 1 (46-153)
Amphibia-Reptilia 00 (2009): 1-22
Biogeographical patterns derived from remote sensing variables:
the amphibians and reptiles of the Iberian Peninsula
N. Sillero
1,∗
, J.C. Brito
2
, A.K. Skidmore
3
, A.G. Toxopeus
3
Abstract. The biogeographic patterns in species density of herptiles were analysed in the Iberian Peninsula. Geoclimatic
regions were identified using a PCA. Individual habitat suitability (HS) models for 23 amphibians and 35 reptiles at 10 × 10
km scale were calculated with ENFA, using 12 environmental factors established with Remote Sensing (RS) techniques.
The species presence proportion in each geoclimatic region was calculated through a cross-tabulation between each potential
occurrence model and the geoclimatic regions. Species chorotypes were determined through Hierarchical Cluster Analysis
using Jaccard’s index as association measure and by the analysis of marginality and tolerance factors from individual HS
models. Predicted species density maps were calculated for each geoclimatic region. Probable under-sampled areas were
estimated through differences between the predicted species density maps and observed (Gap analysis). The selected PCA
components divided the Iberian Peninsula in two major geoclimatic regions largely corresponding to the Atlantic and
Mediterranean climates. The Jaccard’s index clustered herptiles in two main taxonomic groups, with distribution similar
to the Atlantic and Mediterranean geoclimatic regions (7 amphibian + 13 reptile species in three Atlantic subgroups and
16 amphibian + 22 reptile species in four Mediterranean subgroups). Marginality and tolerance factor scores identified
species groups of herptile specialists and generalists. The highest observed and predicted species density areas were broadly
located in identical regions. Predicted gaps are located in north-western, north-east and central Iberia. RS is a useful tool for
biogeographical studies, as it provides consistent environmental data from large areas with high accuracy.
Keywords: ???.
Introduction
Since the Rio Conference of 1992, investigation
in biodiversity is an important goal focussing in
three main research lines: compilation of choro-
logical knowledge (Sillero, Celaya and Martín-
Alfageme, 2005), identification of new species
(Bermingham and Moritz, 1998) and reduction
of biodiversity loss (Wilson et al., 2004). The
latter research line is very important at a world-
wide scale (Houlahan et al., 2000), because the
identification of threatened species and the pro-
posal of conservation measures requires knowl-
1 - Centro de Investigação em Ciências Geo-Espaciais (CI-
CGE) da Universidade do Porto, Departamento de
Matemática Aplicada, R. Campo Alegre, 687, 4169-007
Porto, Portugal
2 - CIBIO, Centro de Investigação em Biodiversidade e Re-
cursos Genéticos da Universidade do Porto, Campus
Agrário de Vairão, R. Padre Armando Quintas, 4485-
661 Vairão, Portugal
3 - ITC, International Institute for Geo-Information Science
and Earth Observation, Hengelosestraat 99, Enschede,
The Netherlands
∗
Corresponding author; e-mail: neftali.pablos@fc.up.pt
edge on species occurrence. However, data on
the composition and spatial distribution of bio-
diversity is largely insufficient, especially for
the worldwide hotspots of biodiversity (Myers
et al., 2000).
Given the present constraints in time and
money for biodiversity assessments, an effi-
cient tool is needed for identifying hotspot ar-
eas and high diversity loss areas (Luoto, Toivo-
nen and Heikkinen, 2002b; Maes et al., 2003;
Lobo, Jay-Robert and Lumaret, 2004). Predic-
tive modelling combined with Geographical In-
formation Systems (GIS) allows the develop-
ment of more robust and reliable models, re-
lating biological diversity with environmental
factors (Brito and Crespo, 2002; Soares and
Brito, 2007; Martínez-Freiría et al., 2008). Cur-
rently they are framework tools for the estab-
lishment of conservation strategies and evalua-
tion of management options (Brito et al., 1999;
Álvares and Brito, 2006; Santos et al., 2006).
Many studies on biodiversity using predic-
tive modelling are frequently performed within
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