INTERNATIONAL CONFERENCE ON WATER MANAGEMENT IN FEDERAL AND
CONFERENCIA INTERNACIONAL SOBRE GESTIÃ“N DEL AGUA EN PAÃSES
FEDERALES Y SEMEJANTES A LOS FEDERALES.
The Situation in Italy
Nicola Lugaresi, Associate Professor,
Trento University Law School
Abstract: This paper describes the situation of water resource management in Italy. It will
first provide some significant data about water, its availability and its use in the national territory
and discuss the constitutional, regulatory and organisational framework of the Italian legal system.
The analysis will then address the different legal components of water resource management and its
relative legal framework. In this sense, water resource management is a complex activity, covering
not only management of water services but other aspects, including ownership, planning and
programming, procedural requirements, qualitative and quantitative protection and economicfinancial
Keywords: water, water resources, river basin district, river basin, management, water
planning, water domain, quantitative protection, qualitative protection, water concessions, soil
protection, water services, water costs.
1. Water resource management: preamble
In Italy the general situation relating to water resources is characterised by a mean availability
that is sufficient but is progressively decreasing; a non-satisfactory qualitative level, above all with
respect to drinking uses; the presence of stress factors both on a qualitative and quantitative level;
and a complex territorial organisational division.1
More specifically with respect to water resource management, the situation of the Italian legal
system is characterised by a relationship between water and law that is not always coherent.2
Traditionally, legal regulation of water in different historical periods, apart from being influenced
by availability and needs, has reflected the evolution of the public interests of the time,3 and has
been conditioned by the classification of water into different legal categories, either traditional or
not. The main interests over public waters are the defence of the territory and population against
water, the use of water resources for civil and production ends and the qualitative and quantitative
protection of water heritage.4 With respect to its classification, water is public property, more
specifically, State property. It is therefore a resource, but also a vital need, an environmental asset
1 GORIA, Alessandra, LUGARESI, Nicola (2004) p. 266.
2 LUGARESI, Nicola (2006) p. 94.
3 GORIA, Alessandra, LUGARESI, Nicola (2004) p. 279.
4 DE BELLIS, Carlo (1984) p. 11.
and a traditional and cultural value,5 which (as particularly demonstrated in international law)
transcends the purely economic aspect, reaching ethical and spiritual levels.6
On a legislative level, there is no consolidated text on water in the Italian legal system; the
different facets of water resources management are disseminated in different regulations. The first
question we must ask and which the Italian legislator still has not seriously answered, is what is
understood by â€œmanagementâ€ of water resources. The term â€œmanagementâ€ appears very often in
regulatory provisions, but it does not explain the elements of the management activity. Section III,
Part 3 of the Legislative Decree 152/2006 is entitled: â€œWater Resources Managementâ€, but this
section, after stating some general principles on water matters, is mainly â€“ if not exclusively â€“
concerned with water services and their management. Water resource management goes much
2. Data related to water resources
In Italy there is no complete, homogeneous and updated repertoire of data related to water
resources; nor has there been a continuous and complete flow of data to a single authority
responsible for compiling, preparing and publishing it. There is no need to underscore how this
deficiency constitutes the first and significant obstacle for water resource management.
The Italian territory is divided into eight River Basin Districts (which, after the last reforms,
group together the 11 former National River Basins, the 18 Interregional River Basins and the other
regional river basins) and into 92 Optimal Territorial Areas (91 of which are currently established)
to manage water services. Optimal Territorial Areas do not, however, always refer to the river
basin as a higher territorial parameter of reference.7
The availability of water resources for different uses â€“ civilian, production and also
environmental â€“ has progressively decreased. Among the most relevant stress factors are the
following. First, the considerable anthropisation of the territory. Italy has a high population density
(more than 59 million residents in 2006, 200 inhabitants per km2, compared with an EU27 average
of 115)8 which continues to grow above all due to the immigration phenomenon. Second, the
intensive livestock and agricultural exploitation (more than 5 million tons of fertilisers marketed in
2006)9. Third, a non-homogeneous productive system from the territorial viewpoint, characterised
in some areas by a considerable proliferation of small and medium enterprises (in 2005, 65
5 LUGARESI, Nicola (1995) p. 1.
6 LUGARESI, Nicola (2000) p. 5; LUGARESI, Nicola (2003) p. 53.
7 CO.VI.R.I. (2008) p. 5.
8 ISTAT (2008) Â§ 12.
9 APAT (2007) p. 62.
enterprises for every 1000 inhabitants, compared with an EU27 mean of 40)10, which may find it
very difficult to adapt their activities to environmental requirements. Finally, the chronic
inefficiency of water services which, although they are subject to rationalisation processes, still
guarantee unsatisfactory qualitative levels (in 2005, only 70% of the water injected into the network
reached the end users)11. The poor legislative and administrative frameworks (with special
reference to the control and monitoring systems) have also contributed to worsening the situation,
creating inefficiency in the public management policies of the national water resources.
On a qualitative level, within a system that divides the quality of water bodies into five
classes (SECA Index â€“ Ecological State of Watercourses, based on the incorporation of chemical
and biological data), the latest available data from the year 2006, reflects a quality level that is at
least sufficient in 78% of the rivers (5% â€œoptimumâ€; 38% â€œgoodâ€; 35% â€œsufficientâ€), compared
within an insufficient state in the remaining 22% (16% â€œscarceâ€; 6% â€œvery badâ€). Although it is not
possible to refer to homogeneous data given that the number of stations monitored is different in
each Region and Macro-Area, the situation between the three Macro-Areas (northern Italy, central
Italy, southern Italy and larger islands) is not too different. With respect to lakes (SEL Index –
Ecological Status of the Lakes, in which five classes are also distinguished) at the least, a sufficient
quality is recoded in 74% of cases (5% â€œoptimumâ€; 29% â€œgoodâ€; 40% â€œsufficientâ€), compared with
an insufficient status in the remaining 26% (23% â€œlimitedâ€; 3% â€œvery badâ€). The situation of
groundwater is more negative. Continuing with a system divided into five classes (SCAS Index â€“
Chemical Status of Groundwater, based on anthropic impact and hydrochemical characteristics) the
2006 data reflects a quality status belonging to the first two classes (high or good hydrochemical
characteristics) in 34% of cases, a good quality state but with signs of worsening in 14% of cases,
and a status of lower quality in 28% of cases (whilst the remaining 24% is represented by resources
submitted to non-existent or insignificant anthropic impact but with special natural hydrochemical
Based on this data the situation does not appear optimal although it does not seem disastrous
either (groundwater being in a more critical position). The data on the classification of surface
water that can be used for drinking is less reassuring. These waters are classified by the Regions
into four categories depending on their physical, chemical and biological characteristics. The
monitoring carried out during the period 2002-2004 indicated that of the 494 surface water bodies
for drinking uses, 81 were situated in category A1 (waters that require a simple treatment), 265 in
A2 (waters that require normal treatment), 113 in A3 (waters that require advanced treatment) and
10 ISTAT (2008) Â§ 45.
11 ISTAT (2008) Â§ 102.
12 APAT (2007) p. 53.
35 in subA3 (waters whose parameters are over the permitted limits, but which can be used in
exceptional circumstances). The most worrying aspect is the tendency towards qualitative
worsening and above all the increase of the waters in category subA3 compared to the previous
On a quantitative level, Italy has more potential resources than the European mean, as the
average rainfall (1950-2000) is 950 mm per year in Italy, compared with 650 mm per year in
Europe.14 The natural surface resources are estimated at 155 billion cubic metres a year and the
total available resources at 50 billion cubic metres a year (that is, which could be used if the
existing infrastructure was efficient).15
Either due to climate reasons or the inefficiency of water services, Italy holds the top position
in the European classification of water abstraction per inhabitant with an average, according to 1999
data, of 740 m2 per year per inhabitant (more than 2000 litres per day) compared with an EU15
mean of 610 m2 per year (less than 1700 litres per day).16 With respect to the distribution of water
consumption, Italy follows a more â€œMediterraneanâ€ model than â€œcommunityâ€ model. In fact, on a
national level, the civil sector absorbs 19% of the water resources (EC level: 14%), the agricultural
sector, 48% (EC: 30%), the industrial sector, 19% (EC: 10%) and the energy sector, 14% (EC:
46%).17 What, in the last instance, distinguishes Italy from the European mean is the percentage of
aquifer abstractions, which is around 23% (EC: 13%), and which basically goes to civil uses.18 The
fact that there are uncontrolled nonpoint source catchments causes highly negative consequences,
one of the most important being the salinisation of waters abstracted near the coast which entails
less agricultural productivity in those areas, thus creating a vicious circle.
Over the last fifteen years, the availability of water resources in Italy has considerably
decreased: faced with a drop in rainfall of 10-15%, surface seepages have decreased by 30% caused
by the intensified water demand.19 In addition, there has been a strong territorial diversification by
Macro-Areas: 65% of the total is abstracted in the north (and 78% with respect to the availability of
the same area), 15% in the centre (52% of the availability), and 20% in the south and in the larger
islands (96% of the availability).20
But the quantitative problem, not so serious in absolute terms per se, worsens not only due to
the qualitative problems mentioned above, but also due to another type of consideration. First, a
13 APAT (2007), p. 70.
14 APAT (2008).
15 A.V.R.I.R. (2006) p. 29.
16 A.V.R.I.R. (2006) p. 40.
17 A.V.R.I.R. (2006) p. 43.
18 A.V.R.I.R. (2006) p. 40.
19 APAT (2007) p. 51.
20 Ministry of the Environment (2002) p. 257.
Deleted: [PAGE REFERENCE?]
limited use of treated wastewater is seen. The re-use of these waters is, in fact, considerably lower
than the European mean, although projects in this regard are increasing. In 2005, the approval of
treatment systems amounted to 80% in sensitive areas and 77% in normal areas (compared with
82% approval of drainage networks in sensitive areas and 78% in normal areas).21 Secondly, the
chronic inefficiency of the water services must be highlighted, due both to infrastructure and
management problems. Water losses in the distribution network (which include both â€œrealâ€ losses,
that is quantities of water injected in the network, but dispersed in the distribution networks before
they reach the delivery point, and â€œapparentâ€ losses, that is, the quantities of water used, but not
billed) reach an average of 38-45% in Italy (with peaks of 50-60% in southern Italy), compared
with much lesser losses in other European countries (20-22% in France, 15-16% in Germany and
the United Kingdom).22
II. Constitutional, regulatory and organisational framework
1. Distribution of legislative power between the State and the Regions (and Autonomous
Italy is a country with a unitary legal system of regional autonomies. Despite the
constitutional review carried out by Constitutional Law 3/2001, which increased the level of
autonomy of the Regions, and the subsequent attempts to establish forms of federalism, Italy, for
the moment, cannot be considered a federal state, but a state with a regional base, within which a
principle of equity is acknowledged between the different territorial levels.23 State reform in a
federal sense, or, in any case, the accentuation of the federal aspects (from the fiscal viewpoint) of
the legal system is one of the basic points of the current Governmentâ€™s program following the April
With respect to the constitutional legal system in force, Italy â€“ one and indivisible â€“
recognises and fosters local autonomies and practices the broadest administrative decentralisation
(art. 5, Const.). Municipalities, Provinces, Metropolitan Cities and Regions are autonomous entities
with their own statutes, powers and functions (art. 114.2, Const.), but of all of these only the
Regions (and the Autonomous Provinces of Trento and Bolzano) have legislative power. Of the
Regions, Friuli-Venezia Giulia, Sardinia, Sicily, Trentino-Alto Adige and Aosta Valley enjoy
21 APAT (2007) p. 73.
22 Ministry of the Environment (2006) p. 17.
23 CARINGELLA, Francesco (2007) p. 700.
special conditions of autonomy (art. 116.1, Const.), regulated by the Statutes approved under the
Constitutional Law. Following the 2001 constitutional reform, other Regions can be recognised as
having other forms of autonomy, through laws of reinforced procedure, based on agreements with
the State (art. 116.3, Const.).
The 2001 reform has also changed the relationship between the State and Regions insofar as
the exercise of the legislative power is concerned, making the Region a body that has residual
competence (art. 117.1, Const.). Art. 117 of the Constitution now contains a list of issues where the
State has exclusive legislative power (art. 117.2, Const.) and a list of issues where the State and the
Regions have joint legislative competence (art. 117.3, Const.), the other issues being relegated to
exclusive regional legislative competence (art. 117.4, Const.). The regulatory power is exercised by
the State only in matters of its exclusive legislative competence, unless delegated to the Regions; in
other issues, the regulatory power is of regional competence, except for the regulatory power of
Municipalities, Provinces and Metropolitan Cities to regulate the organisation and development of
the functions that are granted to them (art. 117.6, Const.).
The lists in art. 117 of the Constitution, which determine the issues that are the exclusive
legislative competence of the State and issues of joint competence between the State and Regions,
do not contemplate water resources. This does not mean that the protection, use and management
of water resources will fall within exclusive Regional competence. In fact, the list of issues of State
legislative competence includes â€œprotection of the environment, of the ecosystem and cultural
assetsâ€, which, if not interpreted too narrowly, would include the vast majority of the water
resources regulation. On the other hand, the list of issues of joint legislative competence includes
issues that have an influence on â€“ or are influenced by â€“ the environmental regulation and the water
resources regulation. These are issues expressed at a high level of abstraction and therefore of
difficult delimitation. Reference is made to issues such as health protection, civil protection, large
transport and navigation networks, production, national transport and distribution of energy and
recovery of cultural and environmental assets.
Thus, the framework derived from the constitutional provisions is complicated and does not, a
priori, permit the identification of certain distribution rules for legislative competence which can be
applied to each case. In this regard, it is the constant intervention of the Constitutional Court, which
both the State and the Regions continuously resort to due to supposed reciprocal invasions of
competence, which defines who the legislative competence corresponds to in connection with
The situation of Regions of Special Statute is somewhat different, but no less complicated.
Exclusive legislative power is no longer just a privilege of these regions, but in the Statutes
(approved under the Constitutional Law and still not amended to be harmonised with the
introduction of the reform) a principle of residuality of State legislative competence is still in force.
Thus, the Statutes generally include a list of issues with exclusive Regional legislative competence
and another list of issues of joint legislative competence, whilst the State has an (exclusive) residual
competence for issues not contemplated.
Constitutional Law 3/2001 also contains a â€œgreater favourâ€ clause for Regions of Special
Statute, by virtue of which, upon the adaptation by the Statutes of these Regions, the provisions of
this law that provide broader forms of autonomy than those already attributed, are applied (art. 10).
In any case, the enumeration of legislative competence contained in the Statutes (and which differ
for each Statute) creates different â€œsubstantialâ€ criteria to those contained in art. 117 of the
Constitution, as generally water is mentioned, but in different areas.24
Basically, the Regions of Special Statute enjoy reinforced legislative autonomy compared
with the other Regions and above all a more specific autonomy with reference to problems related
to water resources. This does not mean that interpretation questions do not arise before the
Constitutional Court, both regarding similar aspects to those that can arise with the other Regions
and the conceptual delimitation of specific matters contained within each Statute.
The difficulty in establishing clear limits between Regional and State legislative powers (with
reference to Regions of Special Statute and other Regions) has compelled the Constitutional Court
to pronounce on more than one occasion. The first decisions on the issue, prior to the 2001
24 The Region of Sicily has exclusive competence in â€œpublic waters, insofar as they are not the subject of public works
of national interestâ€, but also in matters such as â€œagriculture and forestsâ€œ, â€œsanitationâ€, â€œurban developmentâ€, â€œpublic
works, except for the large public works of preferably national interestâ€, â€œsaline lakesâ€, â€œfisheriesâ€, â€œtourismâ€,
â€œlandscape protectionâ€ (art. 14, Const. Law 2/1948). The Region also has joint legislative competence in issues such as
â€œpublic hygiene and healthâ€ and â€œprovision of public servicesâ€ (art. 17, Const. Law 2/1948). The Region of Sardinia
has exclusive competence in issues of â€œexercise of public rights of the Region on public watersâ€ (and â€œsaline lakesâ€),
but also in issues such as â€œagriculture and forestsâ€, â€œsmall sanitation worksâ€, â€œpublic works of exclusive interest of the
Regionâ€, â€œurban developmentâ€, â€œmineral and thermal watersâ€, â€œfisheriesâ€, â€œsaline lakesâ€, â€œtourismâ€ (art. 3, Const. Law
3/1948). The Region has joint legislative competence in issues of â€œmedium and large sanitation worksâ€, â€œelectricity
production and distributionâ€, â€œprovision of public servicesâ€, â€œpublic hygiene and healthâ€ (art. 4, Const. Law 3/1948).
The Region of the Aosta Valley has exclusive competence in issues of â€œpublic waters used for irrigation and domestic
usesâ€ and â€œmineral and thermal watersâ€, as well as in issues of â€œagriculture and forestâ€, â€œlivestock, flora and faunaâ€,
â€œsmall sanitation worksâ€, â€œurban developmentâ€, â€œfisheriesâ€, â€œtourism and landscape protectionâ€ (art. 2, Const. Law
4/1948). The Region can adopt legislative integration and application standards of the State legislation related to
â€œregulation of the use of public waters for hydropower useâ€, â€œhygiene, healthâ€, â€œprovision of public servicesâ€ (art. 3,
Const. Law 4/1948). In the Trentino-Alto Adige Region, it is the Provinces of Trento and Bolzano, and not the Region,
that have significant legislative competences in the water sector. In fact, both provinces have exclusive competence in
issues of â€œmineral and thermal watersâ€, â€œfisheriesâ€, â€œaqueducts and public works of provincial interestâ€, â€œdirect
provision of public servicesâ€, â€œtourismâ€, â€œagriculture, forestsâ€, â€œlivestock and fisheryâ€; â€œsanitationâ€, â€œhydraulic works
of the third, fourth and fifth categoriesâ€ (art. 11, Const. Law 5/1948). Both provinces have joint competence in issues
of â€œuse of public waters, excluding the large diversions for hydropower endsâ€ (art. 12, Const. Law 5/1948). The Region
of Friuli-Venezia Giulia has exclusive competence in issues of â€œagriculture and forestsâ€, â€œsanitationâ€, â€œfisheriesâ€,
â€œaqueducts and public works of local and regional interestâ€, â€œtourismâ€, â€œurban developmentâ€, â€œmineral and thermal
watersâ€ (art. 4, Const. Law 1/1963). The Region has joint competence in issues of â€œuse of public waters, excluding
large diversionsâ€, â€œregulation of public services of regional interestâ€, â€œhygiene and healthâ€, â€œprevention and emergency
work due to natural catastrophesâ€ (art. 5, Const. Law 1/1963).
constitutional reform, focused their attention on the notion of environment, defined as a
constitutional value, a fundamental right of the person and a fundamental interest of the community
(Decision 217/1987 of the T.C.), but also as a unitary intangible asset, with several components to
be protected, even separately (Decision 641/1987 of the T. C.). Returning to the definition of
environment, the Court has recently stated that the environment, as a system which must be
considered in a dynamic manner, is a vital asset with a material and complex nature, the regulation
of which also includes the protection of the equilibrium among the different components (Decision
378/2007 of the T. C.).
After the constitutional reform of 2001 which not only transformed the relationship between
the State and Regions by establishing a closed number of issues of state competence in art. 117 of
the Constitution but also exclusively entrusted the protection of the environment and of the
ecosystem to the State, these decisions take on greater importance. They contribute to defining the
scope of the distribution of the competences between the State and Regions with reference to water
resources management, which, although it does not appear in art. 117 of the Constitution, forms a
substantial part of the environmental issue.
In this regard, the jurisprudence of the Constitutional Court that interprets Constitutional Law
3/2001 did not focus its attention on the on the cross-sectional character of the environment itself.
The new formulation of art. 117 of the Constitution does not forbid the Regions from legislating on
a series of issues related to the environment within the parameter of general principles established
by State law. The Constitutional Court has rejected the idea that the protection of the environment
is identifiable as an â€œissueâ€ in the strict sense and that, therefore, there is a sphere of State
competence that is rigorously circumscribed. On the contrary, the jurisprudence establishes an
unavoidable link with other interests and competences, including those of Regional attribution
(Decision 407/2002 of the T. C.). The â€œcross-sectionalâ€ character of the protection of the
environment means that different competences are expressed, which may even be Regional
(Decision 398/2006 of the T. C). Thanks to the definition of the protection of the environment as a
constitutionally protected â€œvalueâ€, rather than just a simple â€œissueâ€, the State, in agreement with
that value, can establish uniform protection standards in the entire national territory. This then has
an impact on the legislative competences of the Regions (both of Special Statute and others)
(Decision 536/2002 of the T. C).
2. Regulatory evolution: reform of environmental and water resources law
Deleted: mainstreaming of the value of
the environment, by chance
Water regulation has often been developed via parallel channels which sometimes tend to
unavoidably cross over but do not actually form an integrated system. Thus, there is a regulation on
the possible destructive effects of waters, as well as another â€“ qualitative and quantitative â€“ water
protection regulation, another on water services, and another on water concessions. Managing
water resources not only means managing water services, but it also means considering all the
aspects that influence the availability, protection and use of water. The evolution of the regulation
and of the water policies shows the presence of contradictions caused by historical and contingent
factors which have not been totally surpassed.25
In the Italian legal system, the first post-unitary regulation (Law 2248/1865, Annex F) was
concerned with water, especially the execution of public works to defend against it and the natural
phenomena that it causes. The public interest in the exploitation and use of the water resources
became increasingly important after the industrial development process and agricultural demands
made people aware that water is a production means, generating an increase in its value, as well as a
greater interest by the public powers. Consequently the water regulation, as from Law 2644/1884,
progressively dissociated itself from public works regulation, attempting to favour exploitation of
Through partial reforms (D. Lgt. 1664/1916 and 2161/1919), always enacted bearing that
objective in mind, a pathway was followed which led to the publication of a â€œconsolidated textâ€
(Royal Decree 1775/1933) mainly devoted, insofar as water was concerned, to the instrument of
public water diversion concession. The single text of 1933, which also dealt with some aspects of
energy, opened with a definition (teleological, in the way in which it referred to the attitude of water
to serve uses of general public interest) of public waters and therefore implicitly distinguished
private waters. From the legal viewpoint, the new productive demands meant that waters
previously considered private were to be considered public, unless there were of no use for the
public interest. The 1933 regulation, through the use of the concession instrument, established a
public type control and adjustment, the aim of which was the complete exploitation of national
water assets. The concession of public water diversions thus became the main legal instrument to
achieve the economic and productive objectives. However, it very soon showed its incapacity,
outside the planning and programming mechanisms, to properly protect the general public interest.26
For some decades, there were no regulatory developments worthy of mention. Driven by
community law, new legislative developments arose, the main objective of which was protection,
clearly qualitative at first (Law 319/1976) and later quantitative (D. Leg. 152/1999). Law
183/1989, which was principally concerned with soil protection, also incorporated aspects of
25 GORIA, Alessandra, LUGARESI, Nicola (2004) p. 271.
26 GRECO, Nicola (1983) p. 41.
Deleted: on not being subject to use
with a collective scope.
qualitative and quantitative protection, in the reconsideration of the territorial, organisational and
planning order of the sector. D. Leg. 275/1993 amended the concession system, with special
reference to procedural aspects, to make it more efficient and impartial. Law 36/1994 established
provisions of principle relating to the public nature of all waters, the hierarchy between uses and the
application of solidarity criteria in the use of the resource. It regulated water services, introducing
the concept of Integrated Water Service. D. Leg. 152/1999, which replaced the previous regulation
on qualitative protection issues, incorporated quantitative aspects, unlike the previous one, in an
attempt to adopt a more coordinated approach that took into account the other, recently enacted,
regulations, related to soil defence and water services. Thus, after the reforms driven by Law
183/1989, the water resources regulation varies considerably, although gradually and always by
sectors: water concessions, soil defence, water services and qualitative and quantitative protection.
Furthermore, after the enactment of the EC Water Framework Directive (Directive
2000/60/EC) the need has been felt to reclassify and organise the entire regulation. This has
occurred in the form of more general reform of the environmental law, the Law of Delegation
308/2004 and with the subsequent D. Leg 152/2006 (incorrectly referred to as the â€œEnvironment
Codeâ€ or â€œconsolidated text of the environmentâ€, and subsequently amended on several occasions).
The declared objective is to achieve a codification of the environmental law, which was not totally
satisfied, either due to the absence (total in the first instance; partial after its first reforms) of a
â€œstrongâ€ part dedicated to the principles, due to the non-inclusion of some environmental
regulations, or due to the unsatisfactory incorporation of sector regulations that affect the same
With reference to the water sector, although water is no longer considered as a simple asset,
but as an exhaustible resource, to be managed and protected in an integrated fashion, a real
coordination of all the standards on the issue is required. On the one hand, the regulation of the
concessions is outside the D. Leg. 152/2006 (especially in Part Three, dedicated to water), which
basically adopts R.D. 1775/1933 (although considerably amended by the more recent sector
regulations). On the other hand, the Part 3 does not affect the revision of the other regulations on
water (Laws 183/1989 and 36/1994 and D. Leg. 152/1999); rather it presents the sum of them.
There are no common general principles or common definitions or the establishment of a unitary
organisational framework, or other shared standards. The only common aspect is in the title of Part
Three (â€œStandards on soil defence and to combat desertification, protection of water against
contamination and water resource managementâ€). This Part is divided into three sections, devoted
respectively to soil defence and to desertification (Section I), water protection (Section II) and water
resource management (Section III).
The regulation of the water sector continues, therefore, along parallel lines. The 2006 reform
partially and timidly amended the previous legal regime, above all under the umbrella of the
community law, and in particular of Directive 2000/60/EC. But, although now the different
regulations on soil, water protection and water services are contained within one legislative
document (or better said, in one â€œpartâ€ of it), the coordination is only formal. The different aspects
of regulation are still distinct in the structure of D. Leg. 152/2006. It is not correct, either, to define
the Section on water services as a Section dedicated to â€œwater resources managementâ€, because, if
so, it would have an especially reduced field. Water resources are managed at the same time as
their quantity and quality are protected, productive use is regulated and the population is protected
from the possible destructive effects of the watercourses. It is not sufficient to have introduced the
â€œintegrated water serviceâ€ concept; what is necessary now is to introduce the much broader concept
of â€œintegrated water resources managementâ€. The D. Leg. 152/2006 may, in this regard, and
according to a benevolent interpretation, present a first step towards this integration. But, the truth is
that, according to a more realistic interpretation, we have missed the opportunity.
3. Organisational aspects: territorial entities and other organisations
Generally speaking, according to the constitutional dictate, the administrative functions are
attributed in the first instance to the Municipalities, unless, in application of the principles of
subsidiarity, differentiation and appropriateness and related to the scope of interest and the
possibility of exercising those functions efficiently, they are attributed to Provinces, Metropolitan
Cities, Regions and State (art. 118.1, Const.). This does not mean that the vertical principle of
subsidiarity necessarily displaces the exercise of functions downwards, but that a system that
included the functions of regional attribution is replaced with a system that establishes the tendency
for it to be the entities â€œcloserâ€ to the citizens that act, but only if this guarantees a rational
administrative action and an effective decision capacity.
This is the perspective from which the regulation on the distribution of competences in the
legislation of sectors related to water resources must be interpreted, even in the light of art. 3.5 of
the D. Leg. 152/2006. On the one hand, this article enables the Regions to adopt more restrictive
ways of protecting the environment, whenever required by special situations in their territory and
provided that it does not establish any arbitrary discriminations or unjustified procedural unfairness;
on the other hand, it assigns to the State the task of intervening in questions that affect
environmental interests when the objectives of the action foreseen cannot be satisfactorily reached
by the lower territorial government levels.
Furthermore, the organisational regulation has become more complicated due to the presence
of other territorial type distributions, not based on the traditional political and administrative
circumscriptions, but â€“ at least that is the tendency â€“ in hydrographical aspects: River Basin (and
now River Basin District) in the soil defence regulation; and Optimal Territorial Area in the
regulation on water services. The truth is that they are not just simple territorial divisions, as new
bodies have been constituted in them with their own organisations and administrative
responsibilities, such as the River Basin Authority (and now the River Basin District Authority) and
the Area Authority.
D. Leg. 152/2006, which as we have seen includes the majority of the fundamental
regulations on water resources (soil defence; qualitative and quantitative protection; and water
services, but with the regulation of the water concessions still contained basically within R.D.
1775/1933), has made no effort to harmonise the standards on competences. There are no common
regulations, rather, each of the regulations mentioned, contained in separate sections of Part Three
of D. Leg. 152/2006, contains an autonomous distribution of the competences between the different
levels of territorial government (and between the new authorities) that is separated from the rest.
The regulation related to soil defence and combating desertification (Part Three, Section I, D.
Leg. 152/2006) distributes the competences on a central level between the Prime Minister, the
Committee of Ministers for actions in the sector of the soil defence (art. 57, D. Leg 152/2006) and
the Ministry of the Environment (art. 58, D. Leg. 152/2006), identifying in the State-Regions
Conference as the body that must coordinate the most important issues between the State and
Regional level (art. 59, D. Leg. 152/2006). From the technical viewpoint, the Technical Services
and Environment Protection Agency (APAT) exercises functions related to the cognitive and
informative activity (art. 60, D. Leg. 152/2006). When the provisions of the Constitution apply, and
especially the principle of vertical subsidiarity, functions not carried out at State level rest with the
Regions (art. 61, D. Leg. 152/2006), and the definition of the competences of the local bodies
(Municipalities, Provinces, their consortiums or associations and Mountain Communities) and of
the other subjects involved (sanitation and irrigation consortiums, mountain basin consortiums and
other entities of public law) (art. 62, D. Leg. 152/2006). River Basin District Authorities have also
been set up in each River Basin District. These are non-economic public entities that replace the
River Basin Authorities (although in the first application and of doubtful community legitimacy, the
use of the latter was extended, with the relative postponement of the effective establishment of the
former) and which operate according to criteria of efficiency, effectiveness, economy and publicity.
The Permanent Institutional Conference, the Secretary General, the Technical-Operative Secretariat
and the Service Operative Conference are bodies of the River Basin Authority. River Basin District
Authorities are submitted to the management and coordination powers of the Permanent
Institutional Conference (the body, as mentioned above, of the actual River Basin Authority) with
the participation of representatives from several Ministries, interested Regions and the Civil
Protection Department (art. 63, D. Leg. 152/2006).
The regulation on water protection (Part Three, Section II, D. Leg. 152/2006) stipulates a
different organisational approach, less articulated and above all only in broad outline. The State is
to exercise its own competences through the Ministry of the Environment, with the exception of the
competences of the Ministry of Health on hygiene and health, for the Regions and Local
Administrations to carry out their own tasks and functions within the framework of the
constitutionally determined competences and for the sanitation and irrigation consortiums to engage
in carrying out environmental protection and water sanitation actions. Each article of the section
provides a more analytical determination of the specific attributions in the field of the different
functions and the different procedures (art. 75, D. Leg. 152/2006).
The regulation on the water services follows a partially analogous outline. The State
exercises its own competences through the Ministry of the Environment, and the Regions exercise
their functions within the framework of the constitutionally determined competences, with special
reference to the government regulation of the actual territory. With respect to the local bodies, the
functions of their competence related to the Integrated Water Service are carried out through the
Area Authority, a public body constituted in each Optimal Territorial Area and delimited by the
competent Region, where local entities have compulsory participation (art. 148, D. Leg. 152/2006).
Consequently, the organisational framework that arises from analysing the legislation
currently in force is especially complex. D. Leg. 152/2006 has just reproduced the general
framework of the previously applicable regulations related to the distribution of administrative
competences, without any type of coordination. Entering into further detail, we see that there are
more public individuals that interact in the field of these regulations. On the one hand, we find the
traditional territorial entities, which operated according to a modified distribution of competences
model by virtue of the 2001 constitutional reform. On the other hand, we have organisations
created on the model of Anglo-Saxon authorities, but without adopting all of their features, with
special reference to their level of autonomy, and which, among other things, directly emanate from
the actual territorial entities.
III. Water resources management
1. Ownership of the resource: water as public property
The management of an asset does not necessarily presuppose its ownership, but ownership
and management are interrelated. This principle can also be applied to water resources. The
ownership of water and the exercise of the rights related to it have always had a functional value
with respect to management.
Art. 1.1 of R .D. 1775/1933 subordinated the public nature of waters to their capacity to serve
a public use of general interest, the definition of which was subsequently included in art. 822 of
Civil Code, 1942. This did not just have a teleological nature but also an â€œopenâ€ nature, typical of
the notion of public water, capable of covering all the waters, whose use, at a certain moment in
history, in connection with the economic situation and experience, technological development, the
peopleâ€™s needs and the requirements of public powers, could be acknowledged as of public
Decades later, as water was progressively acknowledged as a limited, contaminated and an
increasingly demanded asset, and private waters had been reduced to a mere exception, the
important thing was no longer to specify the content of the public property, but to find the possible
solutions to the water crisis through new governmental, protection and management mechanisms.
In this regard, the general declaration of the public nature of water, included in art. 1 of Law
36/1994 was a relevant novelty (although more from a principled and dogmatic perspective than
from the substantial perspective). The main effect, after exhausting the â€œtheoretic stabilisationâ€
phase has been to definitely transfer attention from the question of ownership, which only had a
functional value, to the question of management and protection.28
The general reserve of each water resource included in Law 36/1994 was later confirmed by
D. Leg. 152/2006, by virtue of which all the surface waters and groundwater belonged to the State.
State ownership of the waters is considered to be closely related to the nature of the waters and to
the relative fundamental principles.29 Water, a resource to be managed according to solidarity
criteria, safeguarding the expectations and rights of future generations to enjoy the same resources
and integral environmental assets, cannot cease to be public property, understanding this property in
a functional sense with respect to the underlying public interests. State ownership of water is
basically the foundation for the regulation of its management, aimed at the rationalisation of uses,
the limitation of waste, fostering the re-use of the resources and the protection of the water assets,
with preference for drinking and civil uses (art. 144, D. Leg. 152/2006).
The objective of the legislator is to guarantee the most complete and rational use of water
resources, of any type and origin. Leaving marginal cases (rainwater and groundwater for domestic
27 CERULLI IRELLI, Vincenzo (1988) p. 1.
28 LUGARESI, Nicola (2006) p. 94.
29 LUGARESI, Nicola (1995) p. 41.
uses, ex art. 163 D. Leg 152/1999) to one side, in some cases, the action of the individual is allowed
and promoted if it may lower the demand of water as an increasingly scarce resource. However, in
all other cases, express consent by the the competent authorities is necessary, issued according to
the forms prescribed by the applicable regulation. Within those procedures the competent
authorities can adapt the specific provisions of the concessions and authorisation so that the public
interest is better served (for example, by imposing additional obligations or duties). The general
declaration of the public nature of water is in practice a more rigid instrument for water
management, subject to fewer dispute possibilities.
Thus, public waters are public assets, a category that traditionally includes those assets which,
based on the combination of a subjective criterion with an objective criterion, belong to public
bodies and are functional with respect to the pursuit of public interests.30 The peculiar regime of
public waters is not so much the consequence of the question of ownership but of the question of
management. Therefore, it is not so important for water to be public insofar as it is of the State,
â€œpropertyâ€ of the State, as conferring the regulation of its use on the State to guarantee its more
rational management and its direct or indirect accessibility, by the community.
Consequently, the Constitutional Court rejected the question of constitutionality that had been
put forward (under articles 2, 3 and 42.3 of the Constitution) with reference to the general
declaration of the public nature by art. 1.1 of Law 36/1994. The illegitimacy was excluded insofar
as the public importance of water was considered to be modified, given that uses are permitted, in
any case, without licence or without a diversion concession, provided that a general interest cannot
be recognised (Decision 259/1996 of the T. C.). The aspect of use, and therefore of management, is
the central and basic element, whilst the aspect of ownership, which in this case is precisely the
object of controversy, has a more formal and functional nature.
2. Planning aspects: planning of the River Basin District and sectorial planning
Regulations related to water resources â€œincludedâ€ in D. Leg 152/2006 also contain different
regimes for the planning and programming of actions. This leads to the possible overlapping of
more planning acts which, although all related to a specific regulation, are mutually influenced by
their relationship with water resources.
The River Basin District Plan that replaces the River Basin Plan after setting up the River
Basin Districts is, like its predecessor, the basic reference plan, and it is regulated in Section I, Part
III of D. Leg. 152/2006. The River Basin District Plan, defined as a territorial sector plan and as a
30 CASSESE, Sabino (1969) p. 260.
Deleted: where the action of the
individual is not only permitted but is
implicitly fostered to create a lower
demand for an increasingly scarce
resource, express consent by
Deleted: For authoritative and
Deleted: public powers
Comment [A1]: I am not sure what
you are saying here. Could you try to
reword these couple of sentences?
Deleted: most important interventions
of the individuals to public interests.
cognitive, regulatory and technical-operational instrument, has an especially broad aim. Thus it
covers the preservation, defence and recovery of the soil, as well as the correct use of water, based
on the physical and environmental characteristics of the interested territory. The contents of the
Plan are analytically specified, and cover cognitive, programming, regulatory, economic, financial
and applicative aspects. The provisions of the River Basin District Plan are immediately binding on
public bodies and private individuals, provided that the plan declares such a feature. The River
Basin District Plan also constitutes parameters to be respected for urban planning. The territorial
plans and regional programmes in agricultural and environmental matters must adapt to the River
Basin District Plan the year after its approval, and the Regions will pronounce action provisions in
the planning sector (art. 65, D. Leg. 152/2006).
The preparation of the River Basin District Plan (which can also be prepared and approved for
sub-basins and for functional sector fragments) requires an especially complex procedure. It is
prepared by the River Basin Authority based on criteria established by the Permanent Institutional
Conference, submitted to strategic environmental evaluation, adopted by the Permanent Institutional
Conference, and finally approved via decree of the Prime Minister and heard at the State-Regions
Conference (art. 66, D. Leg. 152/2006).
Until the approval of the basin plans, the River Basin District Authorities must adopt
abbreviated district plans for hydrogeological planning, which will identify the hydrogeological risk
areas and relative protection measures. The River Basin District Authorities also approve urgent
plans aimed at eliminating situations of high hydrogeological risk, placing priority on areas where a
state of emergency has been declared. They are accompanied by urgent intervention programs to
reduce the hydrogeological risk, urgent emergency plans that contain measures to protect the
integrity of the people affected and infrastructure adaptation plans (art. 67, D. Leg. 152/2006).
Subsequently, River Basin District Plans are implemented through three-yearly intervention
programmes, adopted by the Permanent Institutional Conference. The aim of these programmes is
to carry out ordinary maintenance interventions, provide water policing, internal navigation,
flooding and quick water intervention services, as well as study, instruction and auxiliary activities
(art. 69, D. Leg. 152/2006).
The water protection regulation, contained in Section II, Part III of D. Leg 152/2006, includes
other planning instruments, such as Management Plans and Water Protection Plans, closely linked
to the basin planning.
A Management Plan, defined as internal organisation of the River Basin District Plan, has
been adopted in each River Basin District. It is therefore an abbreviated plan of the latter (art. 117,
D. Leg. 152/2006). Management Plans describe hydrographical aspects, significant impacts and
monitoring activity; they list environmental objectives; they include a synthesis of the economic
analysis, the measures adopted, the controls carried out and the information and public consultation
initiatives and progresses obtained (Appendix 4, Part A, of Part III of the D. Leg. 152/2006).
Water Protection Plans, defined as a specific sector plan, are prepared in agreement with the
objectives on a district scale, and according to the action priorities defined by the Basin Authorities,
after consulting with the Provinces and Area Authorities. The Protection Plan is adopted by the
Regions, after consulting with the Provinces and after adopting possible protection measures. It is
then transmitted to the Ministry of the Environment and the competent River Basin District
Authorities, which will express a binding opinion for subsequent regional approval. The necessary
measures for the integrated, qualitative and quantitative, protection of the water system are the main
aim of the Protection Plan. It also has many other contents: results of the cognitive activity;
environmental quality objectives with a specific destination; lists of water bodies and areas that
demand specific protection measures; sanitation actions; economic analysis (art. 117, D. Leg.
Water basin planning must also be incorporated into the Protection Plans, under the principle
that the quantitative protection of the resource will assist in obtaining quality objectives. The aim
of water use planning is to permit sustainable water consumption and reach the water equilibrium
defined by the River Basin Authorities, bearing in mind the needs, availability, minimum vital flow,
aquifer recharge capacity and use the resource is destined to (art. 95, D. Leg. 152/2006).
Protection Plans are completed later by programs of measures adopted by the Regions and
submitted to the approval of the Basin Authorities (art. 116, D. Leg. 152/2006), which require
additional measures of which quite an extensive indicative list is provided (Appendix 11, Part III of
the Legislative Decree 152/2006).
Finally, the regulation on water services, contained in Section III, Part III of D. Leg. 152/2006
foresees the Area Plan, comprised of four parts: recognition of the infrastructure (which identifies
the actual state of the infrastructure to be entrusted to the Integrated Water Service administrator);
program of actions (which determines the extraordinary maintenance works and the new works to
be carried out); managing and organisation model (which defines the operational structure by which
the administrator guarantees the user the service and the execution of the program of actions); and
the economic-financial plan (which is organised into assets, income statement and balance sheet and
must guarantee obtaining economic-financial equilibrium or, in any case, respect for the principles
of efficiency, effectiveness and economy of the management). The Area Plan is prepared by the
Area Authority and transmitted to the competent Region and to the Ministry of the Environment for
pertinent verification (art. 149, D. Leg. 152/2006).
Deleted: consistency of
The possible overlapping of plans, only included formally in one single legislative document,
but really the fruit of different approaches and regulations, is the greatest obstacle for the water
resources planning and programming framework. Planning, based on true, reliable and updated
data, should be the basis for administrative activity in general and for the managing activity in
particular. But the proliferation of plans, prepared according to different procedures and by
different departments, does not favour a unitary and coordinated approach to the water problem.31
For the legislator, the River Basin District Plan (like the previous River Basin Plan) must be a kind
of â€œsuperplanâ€, where all the typical territorial, environmental and economic issues of the water
sector would converge. The continuous proliferation of plans and programmes, though referring to
the Basin Plan, make it very difficult for the legislator to act. The change from River Basin to River
Basin District is recent (and conflictive) and now requires transforming the River Basin Plans into
River Basin District Plans. Thus it is the first time it has been possible to verify the scope of the
reform, its potential success and the new path planning activity ,may take.
3. Exploitation of resources and water concession system
Public water diversion concession is the traditional instrument through which the Public
Administration permits the use of the water resources by an individual.32 It is still regulated by
R.D. 1775/1933, although it has been amended several times for a one-off device instrument, as is
the concession, to adapt to the integrated management and planning requirements of a less and less
available resource. It is impossible to have integrated water resources management: the concession
instrument has not been inserted into a planning framework which, at a tangentially unitary
moment, bears in mind the availability of the resources, the hierarchy of the interests and the
fundamental demands of the people and it is not limited to the simple watercourse and to the simple
The public water diversion concession is the administrative measure that legitimises the use of
public waters, with some limited exceptions (art. 2, R. D. 1775/1933). Public water users are
subject to the payment of an annual levy, which varies depending on the type of use (art. 35, R. D.
1775/1933). If a watercourse system is modified by natural causes, the State is not compelled to
provide any compensation, apart from the reduction of the levy if the use of the water decreases
(art. 48, R. D. 1775/1933).
Users are divided into large diversions and small diversions depending on the limits
established in agreement with the different users (art. 6, R. D. 1775/1933). Land registries for
31 LUGARESI, Nicola (1995) p. 361.
32 LUGARESI, Nicola (1995) p. 245.
public water users have been prepared in agreement with declarations that users are compelled to
present, which indicate the place, use, quantity of water uses and details of the concession measure
(art. 5, R. D. 1775/1933). To homogenise, update and complete the information system related to
surface water and groundwater and to the relative uses, as well as to the abstractions and returns,
criteria have been established to provide homogeneous State and Regional data mining, including
the data referring to the land registries and to the modalities of access and exchange of data between
public administrations, guaranteeing appropriate ways of informing the public related to the
measures to be taken (art.5-bis, R. D. 1775/1933).
The procedure used to grant water concessions has been modified several times with respect
to the original model, which was characterised by limited preliminary proceedings and a criterion of
temporary preference, based on the chronological order of the arrival of applications. Under the
current legal system, applications for new concessions, accompanied by general projects of works
to be carried out, must be addressed to the Ministry of Infrastructure and be presented at the Civil
Engineering Office. They must also be transferred to the territorially competent River Basin
Authorities, which will express their binding opinion with respect to the compatibility of use with
the forecasts of the Protection Plan, to control the water or hydrological equilibrium. If the River
Basin Authority does not make a decision a Commissioner will be appointed for the matter. The
applications are published so that competitive applications that are technically incompatible with
previous applications can be identified, and for subsequent preliminary proceedings (art. 7, R. D.
1775/1933). The competent authority, guaranteeing the due process principle between the possible
stakeholders, will reflect, in its report, the qualities that characterise the different applications in
connection with the more rational use of the watercourse and the public interests at stake (art. 8, R.
D. 1775/1933). In case of conflicts of interests and incompatibility between more than one
application, preference will be given to the application that guarantees a more rational use of the
water resources depending on different criteria (current level of satisfaction of the basic demands of
the competitors; priority for potable use; real possibility of a better use of the sources in connection
with use; quantitative and qualitative characteristics of the water body; quantity and quality of
returned water with respect to abstracted water). In particular, the preference is that, for the same
type of use, the application should guarantee the greatest return of water in connection with the
quality objectives of the water bodies, or guarantee that the few abstractions demanded should be
comprised of water volumes derived from recovery and recycling activities. For productive uses,
another criterion of preference is the possession of environment management system certifications
(EMAS or ISO 14001). For irrigation, for the same type of use, an application from whoever is the
owner of the lands that must be irrigated or from the relative consortium of owners is preferred. As
a general rule, under equal conditions, preference must be granted to the applicant that will offer the
greatest technical, financial and economic guarantees of immediate execution and use. The
criterion of presentation priority will only be applied when there are no conditions of preference
(art. 9, R. D. 1775/1933).
The granting of the concession, which is accompanied by a drafted regulation that outlines the
concessionaireâ€™s activity modalities, as well as the reciprocal rights and obligations (art. 40, R. D.
1775/1933), is subject to certain conditions to prevent the qualitative and quantitative protection of
the resources from being jeopardised. In particular, the concession cannot be granted if there is a
possibility of the quality objectives defined for the watercourse being harmed; if a minimum vital
flow volume and the water equilibrium is not guaranteed; and if there are economically sustainable
and effective possibilities for the re-use of treated wastewater or of rainwater collected. In any case,
the water volumes granted will adapt to the possibilities of saving, re-use and recycling of the
resources and, in the case of aquifer abstraction, the equilibrium must be guaranteed between the
abstraction and recharge capacity above all to avoid the danger of intrusion of salted or
contaminated water. In this regard, the concession regulation must establish, when technically
possible, the quantity and qualitative characteristics of the returned water (art. 12.2, R. D.
The concession is granted within the limits of the water availability and the concessionaire
cannot allege the concession per se as a title to request compensations from the State (art. 19, R. D.
1775/1933). The rights of use, which cannot be granted without the authorisation of the competent
authority (art. 20, R. D. 1775/1933), generally do not last for more than thirty years (art. 21, R. D.
1775/1933). Large diversions for potable use, irrigation or sanitation, so long as the ends of the
diversion persist and there are no public interest considerations, will be renewed for the
concessionaire, unless the Administration introduces modifications demanded by any new
conditions (art. 28, R. D. 1775/1933).
For a more rational achievement of public interests, interventions can be carried out on
previously approved concessions even before they expire. If a concession application for an
important water use is technically incompatible with other legitimately constituted uses, the
concession can be granted, under the condition that the new concessionaire provides the previous
concessionaires with a relative quantity of water or energy, or, if this is too costly, compensates
them (art. 45, R. D. 1775/1933). On the contrary, the right to divert and use public waters can be
declared null and void if there is a lack of use or misuse, failure to observe the essential conditions
of the concession or legislative and regulatory provisions, lack of payment of the levy or cession
carried out without authorisation (art. 55, R. D. 1775/1933). The possibility of annulling
concessions due to the modification in the evaluation of the public interest in application of general
principles is also outlined.33
D. Leg. 79/1999 establishes a special regime for large hydropower diversion concessions, for
which the Regions and the Autonomous Provinces have competence. Five years before the expiry
of a concession, and in the case of cancellation, relinquishment or revocation, so long as it is
considered that there are no priority public interests in a different use of the water incompatible with
the maintenance of the use for hydropower, a public tender will be called to grant the concession for
payment, lasting for thirty years. The environmental sanitation and improvement of the relative
river basin and the increase of the energy produced or of the power installed are fundamental
elements of the offer. The new concession must respect the minimum vital constant flow of the
watercourses affected, the water security of the basin and the hydropotable use flows relative to
concessions that must be approved by the same water body. The minimum vital constant flow must
be guaranteed even in concessions in force, generating, in the case of reduction of the average rated
power, the right to a single reduction of the concession levy, without compensation for the
concessionaire (art. 12, D. Leg. 79/1999).
Apart from the different regimes, the concession procedure model, even under the current
regulation, has an insurmountable structural limit. It is not able to efficiently evaluate either public
or private interests beyond each specific case, especially if there is a confrontation between
increasingly diffuse and relevant private uses and public uses (even environmental ones). The more
rational use for the specific case, identified after a comparison between several competitive
applications, may guarantee the best decision in connection with the specific case but it cannot
guarantee that this decision will harmonise with the other decisions made in a broader territorial or
administrative scope. The diversion concession does not really permit a global consideration of the
effects produced by the different uses in water resources and, therefore, it is not appropriate to
guarantee the protection of the actual asset on its own. The fact is that the concession regulates the
relationship between individuals and the Administration based mainly on the productive interests of
the former, whilst a correct water management policy requires the prioritised consideration of the
public interests, even preservation, in accordance with the general interest. This does not mean that
the concession instrument has no function, rather that it will have to be framed within a planning or
programming measure where public and private interests can be more globally evaluated.
The reconsideration of the relationships between public interests on water issues is
determined by a change in the actual situation: water is no longer considered an inexhaustible
resource (above all due to the exponential increase in demand) and the contamination phenomena is
33 LUGARESI, Nicola, BERCELLI, Jacopo, FERRAMOSCA, Annalisa (1998) p. 449.
becoming increasingly important and concerning (in many cases limiting the compatible uses). It
can be deduced from this that the productive ends must respect the protection and preservation ends
and that the main problem no longer concerns adapting the demands of the different users, but more
generally, adapting the productive uses to ecological and hydropotable uses.
4. Water resources qualitative and quantitative protection instruments
Water resource management includes and presupposes protection. Protection does not just
mean protection against contamination phenomena, as both qualitative and quantitative protection
must be considered, as included in the most recent community and national regulation.
Section II, Part III of D. Leg. 152/2006 deals with water protection with reference to both
aspects, although the title of the section seems to refer to the qualitative aspects alone. The initial
list of objectives and instruments of the section, confirmed later by the specific contents,
demonstrates that the quantitative aspects are also taken into account (art. 73, D. Leg. D. Leg.
With respect to qualitative aspects, Section II, Part III of D. Leg. 152/2006 is based mainly on
environmental standards and on the prescription of differentiated and reinforced protection areas.
The environmental standards are divided into those that have environmental quality objectives and
those with quality objectives for a specific use. The environmental quality objectives are defined by
reference to connection with the self-treatment capacity of water bodies and the support capacity of
the animal and plant communities. The quality objectives for specific use refer to the ideal status of
the water bodies for a special functional use. Measures and times are defined and coordinated via
protection plans in order to reach certain qualitative levels, without prejudice of the power of the
Regions to identify higher quality objectives and other uses for water bodies (art.76, D. Leg.
152/2006). Surface fresh water used for producing drinking water, water used for bathing activities,
fresh water that requires protection and improvement to be appropriate for the lives of fish, and
water used for the lives of shellfish, are all waters with a specific functional destination (art. 79, D.
With respect to the differentiated and reinforced protection areas, there are more categories:
sensitive areas, which cover a significant part of the national territory; additional sensitive areas can
be gradually established later by the State and the Regions (art. 91, D. Leg. 152/2006); vulnerable
areas caused by agricultural nitrates, where Action Programmes and the provisions of the Best
Agricultural Practices Code must be applied (art. 92, D. Leg. 152/2006); vulnerable areas caused by
plant health products and areas vulnerable to desertification, for which specific protection measures
Deleted: and which can later be
have been applied (art. 93, D. L. 152/2006); protection areas for surface and groundwater destined
for human consumption, divided into absolute protection areas and respect areas (and possible
protection areas), where certain activities are forbidden or permitted with restrictions (art. 94, D.
Leg. 152/2006). Reinforced protection, which contains different requirements for the various
categories both with reference to delimitation of the actual areas and in connection with the
measures to adopt, is justified by specific stress factors that affect these areas and by the destination
of the waters that flow through them.
Qualitative protection of the resource is of course based on the sewer system regime, which is
compulsory for towns with more than 2000 inhabitants (art. 100, D. Leg. 152/2006), but it is also
based on the waste disposal regime, regulated with the respect for the quality objectives of the water
bodies and emission limits (art. 101, D. Leg. 152/2006), and divided into categories (thermal water
discharges; discharges into soil, discharges into subsoil and into groundwater; discharges into
surface waters, discharges of urban wastewater into water bodies of sensitive areas; discharges into
sewer systems; and discharges of hazardous substances). The general rule is that, with few
exceptions (such as discharge of domestic wastewater into sewer systems) all discharges must be
previously authorised (art. 124, D. Leg. 152/2006) and submitted to inspection. The competent
authority (art. 128, D. Leg. 152/2006) is authorised to carry out inspections and extract samples (art.
129, D. Leg. 152/2006) based on a system of programmed, periodical, generalised, effective and
The quantitative protection of water has an autonomous value, connected to the sustainability
of the use of the resources, and also a functional value related to qualitative protection. Section II,
part III of D. Leg. 152/2006 (which, although not always in a coordinated manner, contains some
standards for Section III), apart from considerably modifying some rules of R.D. 1775/1933, is
based on two closely interrelated concepts, water equilibrium and water saving.
The equilibrium of the water balance, pursued through measures contained within the
Protection Plans, is defined by the River Basin Authorities, bearing in mind the needs, availabilities,
minimum vital flow, aquifer recharge capacity and use made of the resource which is compatible
with the characteristics of the water bodies. The data related to the quantitative aspect are collected
via devices to measure the flow volumes and the diverted public water volumes and then placed into
circulation between the competent administrations (art. 95, D. Leg. 152/2006). The equilibrium of
the water balance is also mentioned in Section III, Part III of D. Leg. 152/2006, with a regulation
that partially reproduces that contained in Section II. Here the need is affirmed to guarantee the
equilibrium between the availabilities of resources that can be located or activated in the area of
reference and the needs for the different uses, requesting the competent River Basin Authority to
adopt measures to plan the water economy, and imposing the diversions regulation in such a way as
to guarantee the necessary flow level required for life in the rivers and the equilibrium of the
ecosystems affected (art. 145, D. Leg. 152/2006).
The conceding authorities must contemplate the concession of quantities of water that
guarantee the minimum vital flow (defined by decree of the Ministry of the Environment after prior
agreement with by the State-Regions Conference) in water bodies, for all water diversions. In this
sense, the conceding authorities, after carrying out the census of all the uses that take place in the
same water body, can proceed to review this census, applying temporary or quantitative provisions
or limitations. In both cases, the payment of compensations by the Public Administration is
excluded, except for the relative reduction of the state concession levy (art. 95, D. Leg. 152/2006).
Water saving contributes to obtaining the equilibrium of the water balance. The law imposes
a general and more moral than legal obligation on the administrators and users of water resources,
bearing in mind the absence of specific sanctions. This obligation consists in adopting the
appropriate measures to eliminate waste and reduce consumptions, and increase the recycling and
re-use of resources. The Regions, after hearing the River Basin Authorities, will approve specific
rules on water saving in agriculture (art. 98, D. Leg. 152/2006). With reference to water re-use, the
Ministry of the Environment will establish the technical regulations to re-use waste water, whilst
the Regions will adopt rules and measures to favour water recycling and re-use of treated waste
water (art. 99, D. Leg. 152/2006).
With reference to the water service in particular, it is prescribed that the Regions can adopt
rules and measures aimed at rationalising consumption and eliminating waste, with special
reference to the construction and maintenance of infrastructure, informing and raising awareness of
users, modification of agricultural practices and the harmonisation with urban development
provisions. Furthermore, specific provisions may be adopted on the necessary recovery of losses in
distribution networks and sewer systems. (art. 146, D. Leg. 152/2006).
5. Water services and the Integrated Water Service
Law 36/1994, replaced by D. Leg. 152/2006, posed the objective of rationalising water
services in Italy, characterised by great inefficiency, and in particular by an enormous and
unjustifiable waste of resources. The â€œIntegrated Water Serviceâ€ is comprised of a series of public
catchment, supply, sewer and treatment services, and it must be managed according to principles of
efficiency, effectiveness and saving. The integration of water services is first aimed at overcoming
the fragmentation of management, both vertically (uniting different water services, until then
considered as separate), and horizontally (establishing different operating areas, not limited to the
municipal district), to reach dimensions that will permit business management and economy of
scale. In this sense, Section III, Part III of D. Leg. 152/2006 deals with the management of the
Integrated Water Service (and in general, at least formally, of the water resources) from different
perspectives: environmental protection, competence and basic provision levels of a public service
(art. 141, D. Leg. 152/2006).
The Integrated Water Service is organised in agreement with the Optimal Territorial Areas
defined by the Regions based on physical, demographic and technical parameters. The aim of the
regional delimitation is to progressively improve management of the Service, respecting the
principles of unity of the river basin, unity of management and adaptation of dimensions (art. 147,
D. Leg. 152/2006).
There is an Area Authority in each Optimal Territorial Area, which has its own legal
personality and all local entities of that Territory must partivipate in the Area Authority (according
to different organisational models regulated by the Regions and the Autonomous Provinces). The
exercise of the competences of local entities in water resources matters has been transferred to the
Area Authority, including aspects such as the organisation, concession and control of the
management of the Integrated Water Service (art. 148, D. Leg. 152/2006). Furthermore, the Area
Authority is in charge of preparing the Area Plan (art. 149, D. Leg. 152/2006).
The Area Authority, respecting the Area Plan and the principle of unity of management for
each area, decides the management form of the Integrated Water Service from those set out in the
legal system for local public services: capital society selected via public tender; mixed publicprivate
capital society where the private partner is chosen by public tender; or totally public capital
society, so long as the public body or bodies owning the share capital exercise a similar control over
the society as over their own services and the society carries out the most important part of its
activity with the public body or bodies that control it (art. 113.5, D. Leg. 267/2000).
The Area Authority awards the management of the Integrated Water Service via tender
governed by community provisions and principles, in agreement with the criteria of art. 113.7 of D.
Leg. 257/2000 which refers to the quality, safety, economic conditions, service provision levels,
investment and technological and managerial innovation plans and elements that form an integral
part of the service contract (art. 150, D. Leg. 152/2006).
The relationship between the Area Authority and the Integrated Water Service administrators
is regulated by special agreements, prepared by the Area Authority according to standard
agreements adopted by the Regions and Autonomous Provinces. The minimum content of these
agreements is established directly by the legislator and covers aspects related to the service
Deleted: where the
Deleted: have an obligation to
participate, according to cooperation
forms and modes
management, relationship with users, maintenance of facilities, rates, control system of financial
and insurance guarantees and sanctions. The outline of the agreement prepared by the Area
Authority, with its relative legal system, will be enclosed with the tender specifications. The
service concession is subordinated upon the administrator presenting the appropriate bank
guarantee, which will cover the actions that will be carried out in the five years of management.
The Integrated Water Service contract winner, with the Area Authorityâ€™s authorisation, may manage
other public services that are compatible with it (art. 151, D. Leg. 152/2006). The Integrated Water
Service administrator is entrusted with the water infrastructure belonging to the local entities, which
transfer the relative charges to the administrator (art. 153, D. Leg. 152/2006).
The Area Authority has the power to verify and access the water infrastructures, even in their
construction phase. If there are faults that affect the service, the resource or the environment, the
Area Authority is compelled to appropriately intervene, even exercising substitutive powers, which,
in case of inactivity of the Area Authority, may be exercised by the Regions or the State, through a
commissioner appointed for the matter (art. 152, D. Leg. 152/2006). The Integrated Water Service
administrator is compelled to provide an appropriate territorial control service and an analysis
laboratory for quality controls on the waters, or to stipulate agreements with other water service
administrators (art. 165, D. Leg. 152/2006).
The tariff of the Integrated Water Service, which constitutes the payment for the service
provided, must guarantee integral coverage of the investment and exercise costs. When
determining such a tariff, the quality of the water resource and of the service provided and the
works and necessary adaptations must be taken into account, as well as the amount of the
management costs, the appropriateness of the remuneration of the invested capital and a
contribution to the operating costs of the Area Authority.
Bearing in mind the need to recover the environmental costs according to the â€œpolluter paysâ€
principle, the Ministry of the Environment will define the cost components to determine the tariff
corresponding to the water services for the different water use sectors. In this sense, the Ministry of
Economy and Finance, in agreement with the Ministry of the Environment, will establish the
general criteria for the determination, by the Regions, of the concession levies for the public water
user, with three-yearly updates, always bearing in mind the environmental and resource costs.
Some reductions in levy are foreseen if the concessionaire re-uses the water.
The Area Authority determines the basic tariff. It will be the administrators who will apply
the tariff and collect the payments, always respecting the Agreement and the relative regulation.
Facilities are guaranteed in the tariff modulation for basic domestic consumptions and for
consumptions of certain categories, according to a predetermined income scale, whilst there is the
possibility of increases in tariff for secondary residences, for seasonal tourist complexes, as well as
for craft, commercial or industrial enterprises. The possible tariff grading between the
Municipalities contemplates the investments per capita carried out by the actual Municipalities that
are useful for the ends of the organisation of the Integrated Water Service (art. 154, D. Leg.
Users must pay the tariffs for the public sewer and treatment services, even if there are no
treatment plants or these are inactive. The tariff will not be applied if the user has their own
treatment and collection systems, specifically approved by the Area Authority. To determine the
tariff of the public sewage and treatment services, the volume of water discharged must be
equivalent to the volume of water supplied. For industrial users, the tariff of the sewage and
treatment services is determined based on the quality and quantity of the waste water discharged,
applying the â€œpolluter paysâ€ principle, without prejudice of establishing a reduced tariff for users
who are directly responsible for the treatment and who use the public sewage service, prior specific
approval from the Area Authority. Furthermore, to foster resources saving processes, the tariff for
industrial users is also reduced in agreement with the use of waste waters and used waters in the
production process (art. 155, D. Leg. 152/2006).
The Integrated Water Service administrator also performs the function of informing and
raising awareness of the users, promoting initiatives to disseminate the water culture and
guaranteeing access of the citizens to the data related to the services managed in the Optimal
Territorial Area of their competence. Other advertising methods are foreseen on a State and
Regional level (art. 162, D. Leg. 152/2006).
With a view to planning the use of water resources, wherever there may be a real need to
transfer water between different Regions, beyond the reference perimeters of the River Basin Area,
after consulting with the Regions affected, the River Basin Authorities will promote programme
agreements between them. The works and facilities required will be declared of national interest
(art. 158, D. Leg. 152/2006).
With a view to improving environmental protection, some special provisions have been
included in connection with the protection areas of the water resources for human consumption (art.
163, D. Leg. 152/2006) and national and regional protected natural areas (art. 164, D. Leg.
The Integrated Water Service has constituted a substantial novelty for the Italian legal system,
intervening in a system close to collapse. In any case, it has not solved all the problems related to
water services, either concerning their efficiency, which is still below the European mean, or
referring to the relationship between public and private users and interests. The service
management, even when entrusted to individuals according to the principle of horizontal
subsidiarity, has generally not shown significant improvement margins, but it has posed problems in
the relationship between agent and use. Furthermore, for the tariff establishment mechanism, this
means that the expected progresses have not always been made, with the possible appearance of
new social problems in some territorial areas. The situation gets more delicate if it affects an assetresource
such as water, which is necessary for life and for the dignity of people, and with respect to
which the community can claim expectations for access to it in sufficient quantities and at a
reasonable cost, if not an absolute right. The territorial differentiation of the tariffs, and above all
their quantification, poses a difficult relationship with the basic principles of our legal system, such
as the principle of substantial equality (art. 3.2, Const.) and the principle of solidarity (art. 2,
6. The costs of water
The decreasing amount of water available in the national territory has emphasised its
economic value over the last few years, giving us the right to ask about the need to use market
instruments in water resources management. Considering that it is not just an asset in the legal
sense or a community resource, but rather a social and environmental value and an essential â€œrightâ€
to guarantee peopleâ€™s lives, health and dignity, we cannot blindly leave it in the hands of the market.
If the aspects of social and environmental availability are not considered, disintegration and
separation phenomena can appear, within a system that does not protect the weakest sectors of the
The water services cost recovery problem, as posed by art. 9 of Directive 2000/60/CE, is
incorporated in a regulation introduced into Section II, Part III of D. Leg 152/2006 (in particular in
the section on Management Plans and Water Protection Plans).34 This location is peculiar, if we
consider that it is Section III that deals with water services. The functional relation that the
regulation establishes between the principle of cost recovery and obtaining water quality objectives
is also peculiar. The regulation of costs is not a problem that just affects the water services in a
strict sense, or the qualitative component of protection, but also the management of the resource in
general. These considerations increase the yearning for the systematisation of water-related
regulation, as there is no common part where the provisions of principle that affect the water
resources management can be incorporated in a broad sense.
34 UNNERSTALL, Herwig (2007) p. 29.
In any case, the regulation imposes on the competent Authorities that â€œbear in mindâ€ the
principle of cost recovery of water services, including environmental services and those related to
the resource, applying the â€œpolluter paysâ€ principle and considering the economic analysis carried
out in agreement with Annex 10 of Part III of D. Leg. 152/2006. More specifically, before the year
2010, appropriate water pricing policies must be established to foster a responsible and efficient use
of the water resources by users and to achieve both qualitative and quantitative protection. In
addition, the water services cost recovery must be entrusted to different sectors that use the water
resources (civil, industrial, agricultural), bearing in mind the social, environmental and economic
repercussions, as well as the geographic and climatic conditions. More specifically, whilst the
concession levies for public water diversions bear in mind the environmental costs and resource
costs linked to the use of water, the tariffs of the water services under the responsibility of the
different water use sectors must contribute to cost recovery in agreement with the economic
analysis carried out according to the aforementioned Annex 10 (art. 119, D. Leg. 152/2006). Annex
10 requires the economic analysis to provide sufficient and detailed information so as to be able to
consider the cost recovery principle of the water services, bearing in mind the long-term forecast
and evaluating the effectiveness of the most profitable measures, taking into account the respective
costs, corresponding to the water uses.
In the near future, we can envisage that the water cost question will play an especially
delicate, and even decisive, role, in the area of water resources management systems. Managing
resources also means giving them a value, and this value has not only economic repercussions, but
also social ones, especially from the time when the object of the evaluation is, as occurs with water,
not only an asset, but also a vital need and a productive element.
It can be deduced from examining the scientific data available that the situation is
complicated. The quantity of water available for the different uses is progressively decreasing â€“
above all for potable uses â€“ thus increasing the possibility of the occurrence of water crises. The
strategic type responses to the management of water resources are different, but they have two
aspects in common. The first, of a substantial nature, refers to the need to make the system more
efficient, reducing waste, saving, recycling and re-using the resources, even by increasing the waste
water treatment initiatives. The second, of an organisational nature, demands a real integration of
the system, by simplifying the framework of competences and determining some more rational
The guidelines laid down as priority in the official documents refer to some fundamental
objectives, such as the improvement and integration of the cognitive framework, reduction of the
demand in the different sectors, reduction of pollution, consideration of climate factors and greater
flexibility of management as well as research and training.35 But, without a reconsideration and
simplification of the institutional and regulatory framework, pursuing these objectives will not be at
all easy, and will require greater organisation and procedural efforts, but without being able to
guarantee a satisfactory result. Really, what is still missing is the unitary consideration of the
problems of water resource management, which should cover cognitive aspects, aspects related to
the ownership of the resource, to its planning and programming, aspects related to the exploitation
of the resource, aspects of its qualitative and quantitative protection, aspects related to water
services and aspects related to the application of economic criteria.
Beyond all these considerations is the requirement to finally have a genuine reform of the
water resources regulation, in the area of a water code that is not just a simple sum of previous
regulations, but a real integration of all the rules that affect water management and which is based
on common principles that must currently be sought in the different sectorial parts (and in Directive
2000/60/CE, with special reference to art. 1).
These principles include the public ownership of surface waters and groundwater (art. 144.1,
D. Leg. 152/2006); the hydrogeological sanitation of the territory and the fight against
desertification (arts. 53.1 and 73.1 D. Leg. 152/2006); the nature of water as a resource, which must
be managed according to criteria of solidarity and applying the principle of sustainable development
(art. 144.2, D. Leg. 152/2006); the requirements of qualitative and quantitative protection,
rationalising the uses, limiting waste, reducing consumption, fostering the renovation of resources
and pursuing sustainable and long-lasting uses and saving of the resource (arts. 73.1, 98.1, 144.3,
146 D. Leg. 152/2006); the protection of water as an environmental resource, element and asset, to
be considered with other environmental components, maintaining its capacity to support ecosystems
(arts. 73.1, 144.3, D. Leg. 152/2006); the prevention and reduction of contamination and sanitation
of polluting water bodies (art. 73.1, D. Leg. 152/2006); the hierarchy between the uses, giving
priority to civil uses, and the pursuing an equilibrium in the water balance (arts. 144.4 & 145, D.
Leg. 152/2006); the cost recovery of water services and of water uses, via a one-off economic
analysis that also considers the social, environmental and economic consequences (art. 119.1, D.
Leg. 152/2006); the collaboration of citizens and users, via information, participation and
consultation mechanisms (art. 122.1, D. Leg. 152/2006); and the recovery of efficiency in water
resources (art. 141, D. Leg. 152/2006).
35 APAT (2007) p. 75.
Based on these principles and overcoming the sectorial approach of the water resources
regulation, it will be possible, finally, to reach a genuine code, or consolidated text, for water
resources,36 that will address the different problems in a coordinated manner, posing integrated
water management policies.
CARINGELLA, Francesco (2007), â€œManuale di diritto amministrativoâ€, Milan, GiuffrÃ¨.
CASSESE, Sabino (1969), â€œI beni pubblici. Circolazione e tutelaâ€, Milan, GiuffrÃ¨.
CERULLI IRELLI, Vincenzo (1988), â€œAcque pubblicheâ€, Legal Encyclopaedia, Rome,
Treccani, pages 1-18.
DE BELLIS, Carlo (1984), â€œAcque ed interessi territorialiâ€, Bari, Cacucci.
GORIA, Alessandra, LUGARESI, Nicola (2004), â€œThe evolution of the water regime in
Italyâ€, The evolution of national water regimes in Europe (by Kissling-Naf, I., Kuks, F.), Dordrecht,
Kluwer, pages. 265-291.
GRECO, Nicola (1983), â€œLe acqueâ€, Bolonia, Il Mulino.
LUGARESI, Nicola (1995), â€œLe acque pubbliche. Profili dominicali, di tutela e di gestioneâ€,
LUGARESI, Nicola (2000), â€œRethinking Water Lawâ€. The Italian Case for a Water Codeâ€,
Trento, Department of Legal Science.
LUGARESI, Nicola (2003), â€œDiritto delle acque, principi internazionali, eticaâ€, La disciplina
giuridica delle risorse idriche (por N. Lugaresi, F. Mastragostino) RÃmini, Maggioli, pages 17-78.
LUGARESI, Nicola (2006), â€œAcque pubblicheâ€, Dizionario di diritto pubblico, Vol. I, MilÃ¡n,
GiuffrÃ¨, pages 94-97.
LUGARESI, Nicola, BERCELLI, Jacopo, FERRAMOSCA, Annalisa (1998), â€œRevoca o
modifica delle concessioni idriche per motivi di compatibilitÃ ambientaleâ€, Legal journal on urban
development, pages 449-496.
UNNERSTALL, Herwig (2007), â€œThe Principle of Full Cost Recovery in the EU-Water
Framework Directive â€“ Genesis and Contentâ€, Journal of Environmental Law, pages 29-42.
36 LUGARESI, Nicola (2000) p. 127.
APAT (Agency for the Protection of the Environment and Technical Services), â€œAnnuario dei
dati ambientali 2007 (Tematiche in primo piano)â€, Rome 2007,
APAT (Agency for the Protection of the Environment and Technical Servicesâ€œIdeambienteâ€,
anno 5, n.37, 2008
A.V.R.I.R. (Water Resources and Waste Watch Authority ), â€œRelazione annuale al
Parlamento sullo stato dei servizi idrici, anno 2005â€, Rome 2006,
CO.VI.R.I. (Watch Committee for the Use of Water Resources), â€œRapporto sullo stato di
attuazione dei servizi idrici 2007â€, Rome 2008,
ISTAT (National Statistics Institute), â€œ100 statistiche per il Paeseâ€, Rome 2008,
MINISTERO DEL MEDIO AMBIENTE (Ministry of the Environment and Protection of
Land and Sea), â€œRelazione sullo Stato dellâ€ambiente 2001â€, Rome 2002,
MINISTERO AMBIENTE (Ministry of the Environment and Protection of Land and
Seaâ€œRelazione sullo Stato dellâ€™ambiente 2005â€, Rome 2006,
List of acronyms and abbreviations:
APAT: Agency for the Protection of the Environment and Technical Services
ATO: Optimal Territorial Area
A.V.R.I.R.: Water Resources and Waste Watch Authority
T. C.: Constitutional Court
CO.VI.R.I.: Watch Committee for the Use of Water Resources
D. L.: Decree Law
D. Leg.: Legislative Degree
D. Lgt.: Decreto Lugartenencial
ISTAT: National Statistics Institute
Const. Law: Constitutional Law
R. D.: Royal Decree
Deleted: D. Lug.