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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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