Arguments of the parties
29 The Commission submits that, through its restrictive interpretation of the concept of ‘water services’ within the meaning of Article 2(38) of Directive 2000/60, the Federal Republic of Germany is misapplying Article 9 of that directive, the scope of which concerns the recovery of the costs of those services, the water-pricing policy and the application of the polluter-pays principle to water users.
30 Contrary to the Federal Republic of Germany’s assertions, the concept of ‘water services’ covers not only the supply of water and the treatment of waste water. The very wording of Article 2(38) of Directive 2000/60, its context and the objectives pursued by that directive lead to the conclusion that the definition of those services encompasses other activities such as navigation, hydroelectric power generation and flood protection.
31 In referring to abstraction, impoundment, storage, treatment and distribution, Article 2(38) of Directive 2000/60 lists various activities, one of which must be present in the water service; the use of commas between those terms and the use of the conjunction ‘and’ does not have any other meaning. A water service does not require that all the activities listed in Article 2(38)(a) or (b) of that directive to be present cumulatively.
32 The purpose of that directive is to ensure efficient use of water resources, by providing for adequate participation by the various water services towards the recovery of the costs associated with those water services, in the light of the polluter-pays principle. That purpose would not be undermined if, as the Federal Republic of Germany argues, undertakings involved in water abstraction outside water supply or waste-water treatment activities, such as undertakings involved in open-cast mining in certain Länder, were not required to cover the costs of those abstractions.
33 According to the Commission, Directive 2000/60 and Directive 2004/35 have the same legal basis and both pursue objectives aimed at protecting the environment, which, the Federal Republic of Germany asserts, does not allow for a different interpretation of the concept of ‘Funktion’ found in the German-language version of the latter directive and the concept of ‘Dienstleitung’ found in Directive 2000/60, before going on to infer that the latter refers to human activity. Moreover, in environmental law, services do not presuppose participation by a human being, as observed in the assessment of ecosystem services contained in the Millennium Ecosystem Assessment launched by the United Nations in 2001 (CREDOC, Biotope, Asconit Consultants, 2009).
34 The Commission submits that its broad interpretation of the concept of ‘water services’ does not make the distinction drawn in Article 2(39) of Directive 2000/60 superfluous in its concept of water services. The latter encompasses not only water services but also, more broadly, any activity liable to have a significant impact on water conditions, such as competitive fishing, bathing or navigation on natural water which could not be impounded.
35 The Commission submits that, in those circumstances, the concept of water services covers abstraction for irrigation purposes, which places significant pressure on bodies of water, abstraction for industrial purposes, auto-supply, impoundment for hydroelectric power operations, navigation and flood protection, as well as water storage, treatment and distribution. Yet it would appear that certain Länder, for example, do not charge for abstraction or allow for broad derogations.
36 In the Federal Republic of Germany’s submission, the Commission’s action is based on an incorrect overall approach with regard to Directive 2000/60, in particular the water-pricing structure for water services which, although an important instrument for providing incentive for greater economy and prudence in water resource management, is not the only means provided for in that directive for attaining that objective. The Commission’s interpretations of Articles 2(38) and 9 of Directive 2000/60 nevertheless disregard the management system of that directive, the central idea of which is that water protection requirements in river basins must be weighed up against legitimate rights of use. The Commission thus disregards the existing balance between the various management instruments provided for in that directive as much for reasons of subsidiarity as efficiency.
37 The Federal Republic of Germany submits that the very structure of Article 2(38)(a) and (b) of Directive 2000/60 is based on a clear separation between activities relating to the supply of water and the treatment of waste water. The former are usually necessary stages for the supply of water (acquisition, treatment, storage, routing, distribution); they are set out in detail because it is necessary to specify that those stages must be taken into account in the calculation of costs.
38 The Federal Republic of Germany submits that the concept of ‘water services’ includes not the various activities relating to the supply of water, but rather the supply as a whole. Including those activities in the concept amounts to an unlawful expansion of its scope. That definition does not deprive Directive 2000/60 of its useful effect, which results from a balance between, on the one hand, water protection requirements and, on the other, legitimate uses of water. It may not be inferred from the mere fact that Article 9 of Directive 2000/60 refers to the polluter-pays principle that the obligation to recover costs must be extended to all uses and actions which harm water, since there are other measures specifically laid down such as those found in Annex VI, Part B, to that directive.
39 In order to define the concept of ‘services’, the Federal Republic of Germany considers that the definition given in Article 57 TFEU, which requires a bilateral relationship, should be applied, which is not found, for example, in water use for navigation or flood protection measures, but is established for water supply activities and waste-water treatment.
40 That definition of services is not to be found in Directive 2004/35, which was adopted four years after Directive 2000/60 and does not contain any reference to it in that regard. The German version, moreover, does not refer to ‘Dienstleistung’, but rather to ‘Funktionen’, which does not presuppose human activity. Nor is it to be found in the concept of ‘ecosystem services’, which emerged long after Directive 2000/60.
41 It should also be noted that the Commission’s broad interpretation of the concept of ‘water services’ in reality leads to a denial of the existence of other uses of water, such as those referred to in Article 2(39) of Directive 2000/60. The travaux préparatoires for Article 2(38) of that directive, which shed light on how the latter provisions is to be interpreted, show, inter alia, that the Commission itself had maintained that the principle of recovery of costs was intended to apply only to the supply of drinking water and the treatment of waste water.
42 In their statements in intervention, the Kingdom of Denmark, Hungary, the Republic of Austria, the Republic of Finland, the Kingdom of Sweden and the United Kingdom of Great Britain and Northern Ireland have all submitted observations in support of the forms of order sought by the Federal Republic of Germany.
Findings of the Court
43 It should be borne in mind, as a preliminary point, that in accordance with the Court’s settled case-law, the interpretation of a provision of EU law requires that account be taken not only of its wording and the objectives it pursues, but also its context and the provisions of EU law as a whole. The origins of a provision of EU law may also provide information relevant to its interpretation (see, inter alia, judgment in Inuit Tapiriit Kanatami and Others v Parliament and Council, C‑583/11 P,
EU:C:2013:625
, paragraph 50 and the case-law cited).
44 In the present case, it is clear from the wording of Article 9 of Directive 2000/60 that the Member States are to take account of the principle of recovery of the costs of water services, including environmental and resource costs, having regard to the economic analysis conducted according to Annex III, and in accordance in particular with the polluter-pays principle. Member States must inter alia ensure that water-pricing policies provide adequate incentives for users to use water resources efficiently and thereby contribute to the environmental objectives of Directive 2000/60. Article 2(38) of that directive defines ‘water services’ as comprising all services which provide, for households, public institutions or any economic activity, both abstraction, impoundment, storage, treatment and distribution of surface water or groundwater, as well as waste-water collection and treatment facilities which subsequently discharge into surface water.
45 Those provisions, which do not define the concept of ‘services’, do not make it immediately clear whether the EU legislature intended to make any service relating to each of the activities listed in Article 2(38)(a) of Directive 2000/60, in addition to waste-water treatment activities referred to in Article 2(38)(b), subject to the principle of recovery of costs, as maintained in essence by the Commission, or only those services associated with the supply of water, by requiring account to be taken of all the stages of that activity, as listed in Article 2(38)(a), as well as those associated with waste-water treatment, as referred to in Article 2(38)(b), as contended by the Federal Republic of Germany.
46 It is, therefore, appropriate to begin by analysing the context and overall scheme of the provisions in question in order to ascertain whether cost-pricing is required for all activities associated with the abstraction, impoundment, storage, treatment and distribution of surface water or groundwater, as maintained in essence the Commission.
47 First of all, it is apparent from the travaux préparatoires for Directive 2000/60, as summarised by the Advocate General in points 68 and 69 of his Opinion, that the EU legislature intended, on the one hand, to allow the Member States to determine, on the basis of an economic analysis, the measures to be adopted for the purposes of the application of the principle of recovery of costs, whilst on the other to promote the pricing of those costs, without extending it to all services associated with water use, as practices in the Member States varied widely, inter alia in terms of pricing for water supply services and waste-water treatment.
48 Next, Directive 2000/60, in requiring in Article 9 that Member States are to have regard to the principle of recovery of the costs of water services and ensure that water-pricing policies provide adequate incentives for users to use water resources efficiently and thereby contribute to the environmental objectives of that directive, does not per se impose a generalised pricing obligation in respect of all activities relating to water use.
49 It is therefore necessary to examine, secondly, the scope of those provisions in the light of the objectives pursued by Directive 2000/60.
50 In that regard, it must be noted that Directive 2000/60 is a framework directive adopted on the basis of Article 175(1) EC (now Article 192 TFEU). It establishes the common principles and an overall framework for action in relation to water protection and coordinates, integrates and, in a longer perspective, develops the overall principles and structures for protection and sustainable use of water in the European Union. The common principles and overall framework for action which it lays down are to be developed subsequently by the Member States, which are to adopt a series of individual measures in accordance with the timescales laid down in the directive. However, the directive does not seek to achieve complete harmonisation of the rules of the Member States concerning water (judgment in Commission v Luxembourg, C‑32/05,
EU:C:2006:749
, paragraph 41).
51 As evidenced by recital 19 in the preamble to Directive 2000/60, it aims at maintaining and improving the aquatic environment in the European Union. This purpose is primarily concerned with the quality of the waters concerned. Control of quantity is an ancillary element in securing good water quality and therefore measures on quantity, serving the objective of ensuring good quality, should also be established.
52 Having found that the existing conditions and requirements call for specific solutions, the EU legislature intended, as is apparent inter alia from recital 13 in the preamble to Directive 2000/60, that that diversity of solutions be taken into account in the planning and implementation of measures aimed at ecologically viable protection and use of water in river basins and that decisions be taken at the level as close as possible to the places of use or degradation of water. Consequently, and without prejudice to the importance of water-pricing policies and the polluter-pays principle, as reaffirmed by that directive, priority must be given to actions coming within the jurisdiction of the Member States, in drawing up action programmes adapted to local and regional conditions.
53 Thus, as observed by the Advocate General inter alia in point 72 of his Opinion, Directive 2000/60 is based essentially on the principles of management per river basin; the setting of objectives per body of water; plans and programmes; an economic analysis of the detailed arrangements governing water pricing; the taking into account of the social, environmental and economic effects of cost recovery, and also the geographic and climatic conditions of the region(s) concerned.
54 To that end, Article 11 provides that each Member State must ensure the establishment for each river basin district, or for the part of an international river basin district within its territory, of a programme of measures, taking account of the results of the analyses required under Article 5 of that directive, in order to achieve the objectives established under Article 4 thereof. Under Article 11(3)(b), measures relating to the recovery of the costs for water services, such as those provided for under Article 9 of Directive 2000/60, are among the minimum requirements to be included in such a programme.
55 It is thus clear that measures for the recovery of the costs for water services are one of the instruments available to the Member States for qualitative management of water in order to achieve rational water use.
56 Although, as rightly pointed out by the Commission, the various activities listed in Article 2(38) of Directive 2000/60, such as abstraction or impoundment, may have an impact of the state of bodies of water and are therefore liable to undermine the achievement of the objectives pursued by that directive, it cannot be inferred therefrom that, in any event, the absence of pricing for such activities will necessarily jeopardise the attainment of those objectives.
57 In that regard, Article 9(4) of Directive 2000/60 provides that the Member States may, subject to certain conditions, opt not to proceed with the recovery of costs for a given water-use activity, where this does not compromise the purposes and the achievement of the objectives of that directive.
58 It follows that the objectives pursued by Directive 2000/60 do not necessarily imply that Article 2(38)(a) thereof must be interpreted as meaning that they all subject all activities to which they refer to the principle of recovery of costs, as maintained in essence by the Commission.
59 In those circumstances, the fact that the Federal Republic of Germany does not make some of those activities subject to that principle does not establish by itself, in the absence of any other ground of complaint, that that Member State has thereby failed to fulfil its obligations under Articles 2(38) and 9 of Directive 2000/60.
60 In the light of all the above considerations, the Commission’s action must be dismissed.