The role of spatio-temporal patch connectivity at the landscape level: an example in a bird distribution

Abstract The recent development of landscape ecology emphasizes the importance of connectivity for population viability. Landscape connectivity is the degree to which the landscape facilitates or impedes movement among resource patches. Most of the empirical data identifying landscape spatial patterns (connectedness) that interfere with individual movements, concern walking animals with low powers of dispersal. For flying animals, the distance between patches is measured in almost all cases using euclidean distance. This does not account for the behavioural characteristics of species that depend on landscape patterns for their movements. We hypothesized that the presence of Short-toed Tree Creeper ( Certhia brachydactyla ) depends on landscape spatial structure, so we tested it in two contrasting rural landscapes. These adjacent landscapes differ in grain size, the quality of linear landscape elements delimiting fields, and their history. In the recently reclaimed polder, Tree Creepers are only present in linear rows of trees with a high degree of connection, long enough to support the home range of this bird (supplementation process). Colonisation of this recent landscape from the ‘bocage’, acting as a source of dispersers, required connectedness between hedgerows and planted dykes (source-sink process).

[1]  Ted Baker,et al.  ECOLOGY OF GREENWAYS , 1994, Landscape Journal.

[2]  S. Petit Métapopulations dans les réseaux bocagers : analyse spatiale et diffusion , 1994 .

[3]  P. Clergeau Importance of multiple scale analysis for understanding distribution and for management of an agricultural bird pest , 1995 .

[4]  Paul Opdam,et al.  Bird communities in small woods in an agricultural landscape: Effects of area and isolation , 1984 .

[5]  L. Fahrig,et al.  Habitat Patch Connectivity and Population Survival , 1985 .

[6]  L. Fahrig,et al.  Connectivity is a vital element of landscape structure , 1993 .

[7]  H. Pulliam,et al.  Ecological Processes That Affect Populations in Complex Landscapes , 1992 .

[8]  H.J.W. Vermeulen,et al.  Effectiveness of roadside verges as dispersal corridors for small ground-dwelling animals: A simulation study , 1995 .

[9]  Börje Pettersson,et al.  Extinction of an isolated population of the middle spotted woodpecker Dendrocopos medius (L.) in Sweden and its relation to general theories on extinction , 1985 .

[10]  John A. Wiens,et al.  Scale effects of vegetation on forager movement and seed harvesting by ants , 1994 .

[11]  M. Gilpin,et al.  Metapopulation dynamics: a brief his-tory and conceptual domain , 1991 .

[12]  R. Dennis The Ecology of butterflies in Britain , 1994 .

[13]  W. C. Johnson,et al.  Dispersal of beech nuts by blue jays in fragmented landscapes. , 1985 .

[14]  R. Jongman,et al.  Development of rural areas in Europe: The claim for nature , 1993 .

[15]  F. Burel Time lags between spatial pattern changes and species distribution changes in dynamic landscapes , 1993 .

[16]  M. Villard,et al.  Dynamics in subdivided populations of neotropical migratory birds in a fragmented temperate forest , 1995 .

[17]  S. Boorman,et al.  Group selection on the boundary of a stable population. , 1973, Proceedings of the National Academy of Sciences of the United States of America.

[18]  D. Howard,et al.  Species Dispersal In Agricultural Habitats , 1992 .

[19]  H. Pulliam,et al.  Sources, Sinks, and Population Regulation , 1988, The American Naturalist.

[20]  Richard J. Hobbs,et al.  Nature Conservation 2: The Role of Corridors , 1993 .

[21]  H. Southern,et al.  Handbook of the Birds of Europe, the Middle East and North Africa; the Birds of the Western Palearctic , 1978 .

[22]  L. Hansson,et al.  Dispersal and connectivity in metapopulations , 1991 .

[23]  L. Fahrig,et al.  Conservation of fragmented populations , 1994 .