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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41<br />
2.<br />
3.<br />
the role of evaluation in defining different types of<br />
landscape values: a) consolidated; b) regulative;<br />
c) to be implemented;<br />
consideration of the assessment actions that can<br />
be summed up in the following features which<br />
should be understood as strictly interrelated (Alexander,<br />
2006; Brunetta and Peano, 2003; Brunetta,<br />
2006; Fusco Girard, 1998):<br />
• assessment should be considered a gradual learning<br />
process, as a way of steering assessment<br />
and transformation actions;<br />
• assessment is not only a technical procedure but<br />
also a simultaneous dialogue between institutions<br />
and between institutions and citizens in order to<br />
construct socially shared policies;<br />
• therefore, assessment must not be seen as static<br />
analysis but as a steadily evolving process;<br />
• assessment is not merely an analysis but is oriented<br />
towards the construction of policies in order to<br />
promote sustainable development.<br />
2.The values involved in landscape evaluation<br />
According to the discussion in Brunetta and Voghera<br />
(2008), this methodological perspective complies more<br />
effectively with the aim of determining the value of landscape<br />
resources. Value should be considered a variable<br />
trait that may change over time and assume different meanings.<br />
The role of assessment is to reveal the meanings<br />
and positions that each party attaches to each landscape<br />
resource.<br />
We must assume, of course, that values change<br />
over time but, here, we propose a definition for current<br />
trends that, hopefully, will prove useful for the evaluation<br />
process of landscapes. In fact, some values acquire an<br />
“intrinsic” value, i.e. a value that does not depend on<br />
anything but itself and cannot be related to any other<br />
value and which is therefore independent of the meaning<br />
acquired case by case by other values. Cultural resources<br />
are examples of this type of value. On the other<br />
hand, there are other values that have an “extrinsic”<br />
value.<br />
This distinction between these two types of values is<br />
useful for our discussion from the ELC perspective of<br />
promoting the planning of new ‘landscapes’. In particular,<br />
we should examine the process of definition of “extrinsic<br />
values”, i.e. those that tend to sway decisions regarding<br />
the conservation, rehabilitation, enhancement and transformation<br />
of various landscapes in a territory and which<br />
can be distinguished in the following types (Brunetta and<br />
Voghera, 2007):<br />
• consolidated values refer to the collective identity,<br />
representing the expectations of quality and selfrecognition<br />
of a community of individuals with a<br />
shared conception of life (cultural values, values<br />
of belonging) (Kaplan R., Kaplan, Brown, 1989);<br />
• regulative values originate in the restrictions that<br />
certain elements may impose on certain sites and/<br />
or areas;<br />
• values to be implemented are values that identify<br />
opportunities for landscape improvement as a driving<br />
force for development based on the specificity<br />
of each landscape organization. From this point<br />
of view, the process of legitimizing these types<br />
of “extrinsic” values becomes an indispensable<br />
step in the landscape planning decision-making<br />
process. This process is a public process of<br />
debate that reinforces and strengthens the feeling<br />
of belonging of the parties involved and therefore<br />
the “opportunities” and “interactions” in and of<br />
the landscape. The actions involved in defining<br />
landscape values perform the task of reinforcing<br />
the “bonds” and feeling of belonging among the<br />
various parties. Their aim is to reveal the positions<br />
of the various parties regarding each landscape<br />
resource, to attribute new values to each resource,<br />
to define their positions about each resource<br />
and, at the same time, to broaden each party’s<br />
scope of action and commitment (Jakle, 1987; Higuchi,<br />
1989) However, this act of public identification<br />
of values can be sustained only if assessment<br />
is perceived as a learning process inserted in a<br />
decision-making process (Gorgeu Y., Jenkins C.,<br />
1995). During the assessment, values take shape,<br />
emerge, are made more specific and are defined<br />
in relation to other values.<br />
From this point of view, it is necessary to emphasize<br />
the process of social identification of values before we<br />
can begin to formulate “activist policies” able to blend<br />
the integrated goals of conservation and enhancement.<br />
Without this process, there is no landscape identification<br />
or assessment. For this reason, the value evaluation process<br />
is an essential feature of new landscape planning<br />
approaches.<br />
The ELC implemented a process whereby methods<br />
were to be innovated and advantageous practices were<br />
to be deployed with regard to identifying the quality and<br />
the identities of landscapes. Despite this, we propose a<br />
method for defining articulated development programs for<br />
all landscapes based on the legitimization of “values”.<br />
This is the only way in which such programs can become<br />
engines of sustainable landscape growth and the<br />
growth of territories.<br />
3. The proposal methodology<br />
In the perspective described our proposal methodology is<br />
characterised by integration of the extrinsic values identified<br />
by the research (i.e. consolidated and regulative<br />
values and values to be implemented) and the various<br />
methods of landscape acknowledgement (identification,<br />
interpretation and social legitimization) stemming from<br />
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