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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

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