Pe. Osborne et al., Modelling landscape-scale habitat use using GIS and remote sensing: a casestudy with great bustards, J APPL ECOL, 38(2), 2001, pp. 458-471
1. Many species are adversely affected by human activities at large spatial
scales and their conservation requires detailed information on distributio
ns. Intensive ground surveys cannot keep pace with the rate of land-use cha
nge over large areas and new methods are needed for regional-scale mapping.
2. We present predictive models for great bustards in central Spain based o
n readily available advanced very high resolution radiometer (AVHRR) satell
ite imagery combined with mapped features in the form of geographic informa
tion system (GIS) data layers. As AVHRR imagery is coarse-grained, we used
a 12-month time series to improve the definition of habitat types. The GIS
data comprised measures of proximity to features likely to cause disturbanc
e and a digital terrain model to allow for preference for certain topograph
ies
3. We used logistic regression to model the above data, including an autolo
gistic term to account for spatial autocorrelation. The results from models
were combined using Bayesian integration, and model performance was assess
ed using receiver operating characteristics plots.
4. Sites occupied by bustards had significantly lower densities of roads, b
uildings, railways and rivers than randomly selected survey points. Bustard
s also occurred within a narrower range of elevations and at locations with
significantly less variable terrain.
5. Logistic regression analysis showed that roads, buildings, rivers and te
rrain all contributed significantly to the difference between occupied and
random sites. The Bayesian integrated probability model showed an excellent
agreement with the original census data and predicted suitable areas not p
resently occupied.
6. The great bustard's distribution is highly fragmented and vacant habitat
patches may occur for a variety of reasons, including the species' very st
rong fidelity to traditional sites through conspecific attraction. This may
limit recolonization of previously occupied sites.
7. We conclude that AVHRR satellite imagery and GIS data sets have potentia
l to map distributions at large spatial scales and could be applied to othe
r species. While models based on imagery alone can provide accurate predict
ions of bustard habitats at some spatial scales, terrain and human influenc
e are also significant predictors and are needed for finer scale modelling.