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Landscape – Great Idea! X-LArch III - Department für Raum ...

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insider approach, and that embody “the ability to shift scales<br />

[...], to design relationships between dynamic environmental<br />

processes and urban form” (Corner, 2006: 24).<br />

The question of scale seems to be fundamental both<br />

for the goal sustainability (in terms of dimensional range<br />

of impacts on resources, population involved in sustainable<br />

life styles, scales of intervention) and for the interpretation<br />

and the design of landscape (in terms of geographical<br />

size of the areas, scale of detail, relations with the<br />

observer’s position, range of ecological effects) [Fig.2].<br />

Fig. 2: Scales of sustainability in urban landscapes<br />

scale of urban and site design. A prominent question is<br />

the non-linear, or even contradictory, relation between<br />

the common numerical indicators of sustainability and the<br />

reality of the urban landscape [Fig.1].<br />

Nevertheless by now it seems that <strong>–</strong>in studying and<br />

projecting urban landscapes<strong>–</strong>the application of numerical<br />

indicators does not ensure by itself the achievement of<br />

the goal of sustainability.<br />

Town planning parameters (tree and shrub density,<br />

soil permeability, green public spaces standards, levels<br />

of land consumption etc.), landscape ecology indicators,<br />

statistical indexes related to urban policies (number of<br />

private cars, pedestrian areas, cultural liveliness, use of<br />

bioclimatic building techniques, waste recycling etc.) and<br />

aggregated indicators (Ecological Footprint, Selfsustainable<br />

Local Development Index) are useful consolidated<br />

indicators, but each of them has a view on a single<br />

dimensional scale (the building, the city, the region or the<br />

national scale) and on a single time of collection (and<br />

they are often gathered at different time/date). Besides,<br />

institutions holding the data may be biased towards certain<br />

types of data, causing inaccuracies in data collection<br />

and display.<br />

Assuming the need of “exploring alternative models<br />

for understanding the sustainability of systems [...] in a<br />

more responsive learning mode” (Dahl, 2008: 42), the<br />

research will try to assess if and how numerical indicators<br />

could give way to those methods of “understanding<br />

sites by means of fieldwork analysis”, trying to investigate<br />

the “unlimited number of scales” in which a site exists<br />

(Pollack, 2006: 130) and considering landscape as the<br />

medium through which contemporary cities develop and<br />

communicate themselves, encouraging more or less<br />

sustainable lifestyles (DETR, 2000:53).<br />

The research starts with an overview on the various<br />

methods of studying urban landscape used in those disciplines,<br />

such as landscape architecture, geography, geoanthropology<br />

and landscape urbanism, that combine a quantitative,<br />

analytical approach and a qualitative, analogical,<br />

The research has since now collected the interpretative<br />

keys of urban landscapes which are commonly used in<br />

the above mentioned disciplines to describe and interpret<br />

the spatial configuration of the urban settlement,<br />

the architectural body of the city, the legibility of urban<br />

spaces, the presence of natural elements in the urban<br />

hierarchy and the different uses and users of urban<br />

spaces. Besides, these interpretative keys have been<br />

critically related to consolidated targets of sustainability<br />

(derived from the sets of the Expert Group on the Urban<br />

Environment of the European Commission, the European<br />

Council of Spatial Planners and the European HQE2R<br />

project) and they are now being tested on various types<br />

of projects and practices of urban transformation (postindustrial<br />

sites redevelopment, brownfield remediation,<br />

new green infrastructures, management of urban fringe<br />

areas, etc.).<br />

Nested scales in urban landscape<br />

In the investigation of the sustainability of urban transformation<br />

through the lens of landscape, three features are<br />

emerging.<br />

First of all, the feature of multiscalarity or, better, the<br />

presence of nested scales in the structure of urban<br />

landscape, as introduced by Henri Lefebvre and recently<br />

suggested in the discipline of <strong>Landscape</strong> Urbanism (Pollack,<br />

2006: 129). In the diagram [fig. 3], the private scale,<br />

the medium or transitional scale and the global scale are<br />

deeply interrelated and internally differentiated: hierarchies<br />

of scales do exist but they are not fixed or singular.<br />

When bringing into action this Lefebvre’s diagram in the<br />

work of reading and projecting landscapes, it appears<br />

that “the potential of a project to operate at different scales<br />

relies on a designer’s investment in representing the<br />

elements and forces that exist or have existed at those<br />

scales, as a precondition for designing ways to foster<br />

interdependencies between them” (Pollack, 2006: 130).<br />

With this nested scale approach, the study of existing<br />

Fig. 3: Diagram of nested scales (adapted from: Pollack, 2006)<br />

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