PDF 20.134kB - TOBIAS-lib - Universität Tübingen
PDF 20.134kB - TOBIAS-lib - Universität Tübingen
PDF 20.134kB - TOBIAS-lib - Universität Tübingen
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Landscape fragmentation<br />
Pattern-related impacts<br />
Surface-related impacts<br />
Land use pattern<br />
Journal of Land Use Science 79<br />
Loss/degradation of<br />
prime farmland<br />
Surface<br />
characteristics<br />
Negative impacts on<br />
aquatic systems<br />
Higher development costs<br />
(infrastructure)<br />
Contribution to urban<br />
heat island<br />
Less cost-efficient public<br />
transit<br />
Higher travel distances<br />
Automobile dependence<br />
Urban density<br />
Impacts/outcomes<br />
(examples)<br />
Density-related impacts<br />
Figure 1. Impact phenomena caused by changes of land cover (surface), land use pattern and density.<br />
Naess 2003). In addition, pattern sprawl is one crucial contributor to landscape fragmentation<br />
characterised by a process of perforation, dissection and isolation of habitat areas and<br />
natural or semi-natural ecosystems (Jaeger 2000). Many scholars regard fragmentation as a<br />
major cause of the alarming loss of species all over the world (Theobald et al. 1997;<br />
Cieslewicz 2002).<br />
Furthermore, sprawl can be characterised by its change of land use composition. We<br />
address this as the ‘surface dimension’ of sprawl. Urban sprawl describes a large scale<br />
conversion process of agricultural, natural or semi-natural surfaces to built-up areas with a<br />
high share of artificial, impervious surfaces and complex effects on ecological systems<br />
(Schueler 1994; Arnold and Gibbons 1996; Moglen and Kim 2007). ‘Surface sprawl’ usually<br />
affects the core areas of metropolitan areas and their near surroundings. Next to the amount of<br />
urbanised land or impervious surfaces, the quality of land that became urbanised within a<br />
specific period of time has to be taken into account (e.g., soil quality, habitat quality). Of<br />
particular concern is the loss of prime agricultural land due to its importance for the long-term<br />
competitiveness and sustainability of agriculture (Hasse and Lathrop 2003).<br />
For all three dimensions, we propose specific indicators presented in the subsequent section.<br />
3.2. Methodology<br />
Table 3 gives a brief overview over the selected indicators. ‘Indicator description worksheets’,<br />
summarised in Annex 1, provide detailed information on the actual implementation (calculation,<br />
data sources, base years). The main intention in this selection is a comprehensive and