planning, and to the absence of true coordination between all sectoral instruments
concerning rivers, and surface and underground waters management. In this sense,
the RC is identified as a liaising tool between the two spheres of planning, as well
as a solution to any possible overlap in institutional and legal competences of the
actors involved, or between the actions and interventions envisaged by different
programs and plans.
Undoubtedly, the specific potential inherent to RC must also come to terms with
the different national and local regulatory frameworks that establish the degree of
integration between integrated basin management and spatial planning. For
example, in France the relations between contrats de rivière (CdR) and urban and
territorial planning tools are decidedly strengthened by the constraint that the latter
be coherent with the Schémas Directeurs d’Aménagement et Gestion des Eaux
(SDAGE) and Sché mas d’Aménagement et Gestion des Eaux (SAGE), as seen in the
previous chapters. Therefore, basin plans give every assurance of effective synergy
between the different sectoral programming instruments, representing the common
regulatory framework of reference for both CdR and spatial planning tools.
The French example illustrates how RC prove instrumental in operatively and
progressively assembling the functional mosaic of integrated basin planning and
management, enabling an effective and lasting restructuring of an entire system of
territorial, social, economic and cultural relations between up-stream and
down-stream areas and communities. Moreover, in those contexts in which a SAGE
is not yet in force, the reflection and actions underlying the implementation of a
CdR may actually serve as the groundwork that sets the stage for the procedures that
may bring to the adoption of a SAGE.
The analysis of experiences carried out in Europe, especially in France and Italy,
clearly shows how RC should hardly be considered a mere sectoral tool, relevant
only to the protection and management of water resources, but rather a generative
process that spans the domains of hydrography, hydrogeology, ecology, sociology,
economics, public health and culture.
Inasmuch as they constitute contractual agreements among public and private
promoters and other participating stakeholders, RC can be tailored, depending on
the case, to multiple fields of action relative to the thematic areas of specific local
interest. For example, in addition to actions aimed at safeguarding and re-qualifying
fluvial environments, initiatives for improving the quality standards of water
resources may also be prompted along with others to sustain the production
capacity of the agricultu ral, fishing and energy sectors. Similarly, purely technical
measures related to contrasting geological risks can be coupled to initiatives seeking
to bridge gaps in the overall knowledge base regarding specific hydrographic and
territorial regions. For example, through an interdisciplinary approach, the struc-
tural and infrastructural dimension of a RC plan of actions may be integrated by
conducting a census and determining the collective recognition of the component
parts of individual entities of naturalistic interest (biodiversity, ecological networks,
parks, reserves), anthr opological and cultural interest (cultural herit age, historic
built-up areas, cultural landscapes) and social interest (identity elements, gathering
places, recreational areas), and their interdependencies (Magnaghi 2011). In
5 Final Considerations and Open Scenarios 111