Modelling landscape-scale habitat use using GIS and remote sensing: a casestudy with great bustards

Citation
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
Citations number
63
Categorie Soggetti
Environment/Ecology
Journal title
JOURNAL OF APPLIED ECOLOGY
ISSN journal
00218901 → ACNP
Volume
38
Issue
2
Year of publication
2001
Pages
458 - 471
Database
ISI
SICI code
0021-8901(200104)38:2<458:MLHUUG>2.0.ZU;2-Q
Abstract
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.