A potential habitat network for the Eurasian lynx Lynx lynx in Scotland

1The severe and early destruction and fragmentation of woodland habitats due to human activities is thought to have been a leading factor in the extirpation from Britain of several large, forest-dependent mammal species, such as the Eurasian lynx Lynx lynx. However, during the 20th century, Scotland in particular has experienced rapid, large-scale reafforestation. In order to assess if this reafforestation has been sufficient to permit the potential restoration of extirpated forest mammal species with large spatial requirements, a Geographical Information System (GIS) analysis of potential habitat of one species, the Eurasian lynx, was performed for the Scottish mainland. 2A rule-based analysis, incorporating data and expert opinion from Switzerland, an environmentally similar area where lynx now occur, was used to identify patches of suitable lynx habitat in Scotland. A connectivity analysis was used to investigate whether and how these patches are connected to form larger interconnected networks of potential lynx habitat that would allow lynx to sufficiently interact with one another to form a single interbreeding population. 3Scotland has over 20 000 km2 of suitable lynx habitat split into two main networks of interconnected patches: the Highlands (c. 15 000 km2) and the Southern Uplands (c. 5000 km2). A further 800 km2 of potential habitat, contiguous with the Southern Uplands lynx habitat network, lies across the border in England. Although connectivity between the Highlands and Southern Uplands networks is currently weak, the implementation of measures to mitigate the barrier effects of busy roads in central Scotland could facilitate the movement of lynx between the two areas. 4Based on the availability of prey resources, Scotland could support around 400 adult and subadult lynx in the Highlands and around 50 in the Southern Uplands. A Scottish population of this size would be the fourth largest lynx population in Europe considering current population estimates.

[1]  M. Gorman,et al.  Using prey densities to estimate the potential size of reintroduced populations of Eurasian lynx , 2007 .

[2]  Thorsten Wiegand,et al.  Fragmented landscapes, road mortality and patch connectivity: modelling influences on the dispersal of Eurasian lynx , 2004 .

[3]  P. Ferreras Landscape structure and asymmetrical inter-patch connectivity in a metapopulation of the endangered Iberian lynx , 2001 .

[4]  D. Macdonald,et al.  Simulating the proposed reintroduction of the European beaver (Castor fiber) to Scotland , 2000 .

[5]  Thorsten Wiegand,et al.  Assessing the suitability of central European landscapes for the reintroduction of Eurasian lynx , 2002 .

[6]  C. Breitenmoser-Würsten,et al.  Action Plan for the conservation of the Eurasian Lynx (Lynx lynx) in Europe , 2000 .

[7]  J. Malo,et al.  EFFECTIVENESS OF WILDLIFE CROSSING STRUCTURES AND ADAPTED CULVERTS IN A HIGHWAY IN NORTHWEST SPAIN , 2003 .

[8]  Thorsten Wiegand,et al.  RULE-BASED ASSESSMENT OF SUITABLE HABITAT AND PATCH CONNECTIVITY FOR THE EURASIAN LYNX , 2002 .

[9]  E. Revilla,et al.  Lynx reintroductions in fragmented landscapes of Germany : Projects with a future or misunderstood wildlife conservation? , 2005 .

[10]  F. Zimmermann,et al.  Status and conservation of the Eurasian lynx (Lynx lynx) in Europe in 2001 , 2004 .

[11]  Paul Opdam,et al.  Designing a Coherent Ecological Network for Large Mammals in Northwestern Europe , 2003 .

[12]  K. Schmidt,et al.  Foraging by lynx and its role in ungulate mortality: the local (Białowieża Forest) and the Palaearctic viewpoints , 1993 .

[13]  Jana Verboom,et al.  Dispersal and habitat connectivity in complex heterogeneous landscapes: an analysis with a GIS based random walk model , 1996 .

[14]  A. Ward Expanding ranges of wild and feral deer in Great Britain. , 2005 .

[15]  C. Wilson Could we live with reintroduced large carnivores in the UK , 2004 .

[16]  K. Schmidt Maternal behaviour and juvenile dispersal in the Eurasian lynx , 1998 .

[17]  U. Breitenmoser Large predators in the Alps: The fall and rise of man's competitors , 1998 .

[18]  Fridolin Zimmermann,et al.  Testing expert groups for a habitat suitability model for the lynx Lynx lynx in the Swiss Alps , 2007 .

[19]  Anthony P. Clevenger,et al.  Highway mitigation fencing reduces wildlife-vehicle collisions , 2001 .

[20]  R. Tiedemann,et al.  Bisoniana 117. Mitochondrial DNA-RFLP analysis reveals liw levels of genetic variation in European bison Bison bonasus , 1998 .

[21]  Peter W. W. Lurz,et al.  Modelling the distribution of the red and grey squirrel at the landscape scale: A combined GIS and population dynamics approach , 1997 .

[22]  John F. Lehmkuhl,et al.  Landscape permeability for large carnivores in Washington: a geographic information system weighted-distance and least-cost corridor assessment. , 2002 .

[23]  F. Zimmermann,et al.  Natal dispersal of Eurasian lynx (Lynx lynx) in Switzerland , 2005 .

[24]  H. Haller,et al.  Zur Raumorganisation der in den Schweizer Alpen wiederangesiedelten Population des Luches (Lynx lynx.) , 1985 .

[25]  F. Zimmermann,et al.  Potential distribution and population size of the Eurasian lynx Lynx lynx in the jura Mountains and possible corridors to adjacent ranges , 2007 .

[26]  T. Lord,et al.  New evidence for the occurrence of Eurasian lynx (Lynx lynx) in medieval Britain , 2006 .

[27]  D. Yalden The History of British Mammals , 1999 .

[28]  H. Schmidt-Posthaus,et al.  CAUSES OF MORTALITY IN REINTRODUCED EURASIAN LYNX IN SWITZERLAND , 2002, Journal of wildlife diseases.

[29]  Charles R. Warren Managing Scotland's Environment , 2003 .

[30]  M. Delibes,et al.  Use of Non-Wildlife Passages Across a High Speed Railway by Terrestrial Vertebrates , 1996 .

[31]  R. Forman,et al.  ROADS AND THEIR MAJOR ECOLOGICAL EFFECTS , 1998 .