Iberian Lynx in a Fragmented Landscape: Predispersal, Dispersal, and Postdispersal Habitats

By Francisco Palomares, M. Delibes, P. Ferreras, J. M. Fedriani, Javier Calzada, E. Revilla. 2000

163 citations recorded by the source corpus.

View Paper: https://www.semanticscholar.org/paper/380c8fbf33d26c06cdb19c44216095d963a1443f

How researchers see this paper

The researchers whose trusted networks rank it highest, strongest advocate first. Every researcher gets a different order.

Citations in the corpus

Habitat suitability, corridors and dispersal barriers for large carnivores in Poland (2010, background): “This assumption is supported by the fact that, in the Iberian lynx, dispersing individuals used some habitats according to their availability whereas the same habitats were avoided by adult residents (Palomares et al. 2000).”
Proximate and ultimate causes of dispersal in the Iberian lynx Lynx pardinus (2004, methodology): “Dispersing lynxes may use habitats of lower quality than those used by resident lynxes, although dispersers avoid open habitats such as marshes and croplands (Palomares et al., 2000).”
Spatial ecology of the European wildcat in a Mediterranean ecosystem: dealing with small radio‐tracking datasets in species conservation (2009, methodology): “Only classes with availability above 5% were considered for analysis (Palomares et al., 2000).”
Young flying squirrels (Pteromys volans) dispersing in fragmented forests (2004, background): “Similarly, it has been found that dispersing juvenile Iberian lynx individuals seem to use habitats of lower quality than do resident individuals (Palomares et al., 2000).”
Fragmented landscapes, road mortality and patch connectivity: modelling influences on the dispersal of Eurasian lynx (2004, unknown): “We thus defined any forested area and breeding habitat as preferred dispersal habitat (see Schmidt 1998; Palomares et al. 2000).”
Habitat use by Oncifelis guigna and Pseudalopex culpaeus in a fragmented forest landscape in central Chile (2004, background): “Nevertheless, pine plantations placed around native forest are not an abrupt boundary (Palomares et al. 2000), as they are utilized by O. guigna, but it depends on how close they are to forest (Estades and Temple 1999).”
Designing a Conservation Landscape for Tigers in Human‐Dominated Environments (2004, result): “This assumption is supported by field studies of radio-collared cougars (Beier 1995; Sweanor et al. 2000) and lynx (Palomares et al. 2000), both of which will disperse through low-quality corridors.”
Effectiveness of terrestrial protected areas in reducing habitat loss and population declines (2013, background): “However the importance of broad site-level management even for single-species conservation has been highlighted by several studies (Forrest et al., 2012; Liu et al., 2001; Palomares et al., 2000) and site-level interventions constitute the majority (80”
Vegetation structure and prey abundance requirements of the Iberian lynx: implications for the design of reserves and corridors (2001, background): “Plantations are very frequently used by dispersing lynx (Palomares et al. 2000).”
Making the matrix matter: challenges in Australian grazing landscapes (2005, background): “Despite the special situation of semi-aquatic organisms, animals that do not undergo major biological changes throughout their life history can also undergo changes in habitat use depending on their age (e.g., pre- and postdispersal habitat; see Palomares et al. (2000) for an example of the Iberia”
RULE-BASED ASSESSMENT OF SUITABLE HABITAT AND PATCH CONNECTIVITY FOR THE EURASIAN LYNX (2002, background): “Other quantitative large-scale habitat analyses of large carnivores have also shown that one key resource alone can sufficiently describe the favorable habitat (e.g., Mladenoff et al. 1995, Mladenoff and Sickley 1998, Palomares et al. 2000, Schadt et al. 2002).”
Assessing the suitability of central European landscapes for the reintroduction of Eurasian lynx (2002, background): “The future of large carnivores in central Europe will depend on our ability to protect and promote suitable areas and connecting corridors where they can be managed effectively (Corsi, Duprè & Boitani 1999; Palomares et al. 2000; Palomares 2001).”