Changes and interactions between forest landscape connectivity and burnt area in Spain

详细信息    查看全文

• 作者：Carmen Martí ; n-Martí ; n^a ; Robert G.H. Bunce^b ; ^c ; Santiago Saura^d ; Ramó ; n Elena-Rosselló ; ^a ; ^{ramon.elena.rossello@upm.es}
• 关键词：Conefor-Sensinode ; Ecological connectivity ; Landscape dynamics ; Sispares ; Spatial pattern indicators ; Wildfire occurrence ; Farm intensiveness ; Rural population density
• 刊名：Ecological Indicators
• 出版年：2013
• 出版时间：October, 2013
• 年：2013
• 卷：33
• 期：Complete
• 页码：129-138
• 全文大小：2006 K

文摘

The spatial structure, functionality and dynamics of forest landscapes in peninsular Spain and the Balearic Islands were compared over the last five decades. Two particular features were studied in the sample sites: forest connectivity for wildlife and areas burnt by wildfires. 191 Squares, each 4 km ¡Á 4 km, were selected from the SISPARES (the monitoring framework designed to evaluate the trends in the structure of Spanish rural landscapes) environmental strata. Aerial photographs from 1956, 1984, 1998 and 2008 were interpreted and 11 land cover categories mapped and checked in the field, using a minimum mapping area of one hectare. The Equivalent Connected Area Index was used to assess forest connectivity over the sampling period. Social and economical factors were assessed using indicators of farm intensiveness. The Spanish forest connectivity has improved in the last five decades although two different trends can be identified: the first 40 years are characterized by positive rates of growth whereas the 10 last years are characterized by their stability. Nevertheless the area of burnt land was higher along the first 25 studied years and decreased significantly over the last decade.

Our results show the climate is the main driver in the evolution of forest connectivity and burnt area in the forest landscapes, playing a direct role on forest biomass production and wildfire ignition and propagation, as well as an indirect role by keeping vertical and horizontal forest continuity through the landscape spatial pattern. Social and economic factors are very important drivers as well: Rural population density and farm size average have been tested as good indicators of landscape artificiality, highly correlated to wildfire hazard and forest connectivity.

Finally, we have pointed out the evolutionary path followed by SISPARES framework as a tool for monitoring rural landscapes. It emphasises on the requirement of a 30 years time window for building-up reliable dynamic multifunctional model.