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