C-392/96
ECLI:EU:C:1998:612
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OPINION OF MR LA PERGOLA — CASE C-392/96
OPINION O F ADVOCATE GENERAL LA PERGOLA delivered on 17 December 1998 *
I — Introduction 3. After examining that legislation, the Commission sent Ireland a further letter of formal notice on 7 November 1991, to which the Irish Government replied by letter of 12 May 1992. 1. Within a few months of its judgment of 22 October 1998 in Case C-301/95 Com- mission v Germany [1998] ECR I-6135, the Court is again called upon to rule on the correct transposition into national law of Council Directive 85/337/EEC of 27 June 4. On 28 April 1993 the Commission 1985 on the assessment of the effects of delivered a reasoned opinion in which it certain projects on the environment (here- alleged that Ireland had failed: inafter 'the Directive'). 1The question to be addressed in the present case is whether Ireland has adopted the necessary measures to ensure the correct transposition of the Directive into its national legislation. (a) to transpose Article 3 of the Directive;
(b) correctly to transpose Article 4(2) of I I— The pre-litigation stage the Directive or Annex II thereto;
2. On 13 October 1989 the Commission sent Ireland a letter of formal notice, in accordance with the procedure laid down (c) to make proper provision for the in Article 169 of the EC Treaty. In exemptions provided for in Article 2(3) response, Ireland sent the Commission of the Directive; copies of the Irish legislation transposing the Directive into national law (S.I. No 349 of 1989 and S.I. No 25 of 1990).
* Original language: Italian. (d) correctly to define the information to 1 — OJ 1985 L 175, p. 40. be provided by the developer in
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accordance with Article 5 of the No 101 of 1996. Yet more correspondence Directive; ensued regarding Complaint No P 95/4724 concerning afforestation and Complaint No P 95/4219 concerning peat extraction.
(e) correctly to define the information to be provided to the public in accordance with Article 6(2) of the Directive; Legal analysis
6. The present dispute concerns the mea- sures adopted by Ireland for the transposi- tion of the Directive into national law. (f) correctly to define the information to be provided to the other Member States in accordance with Article 7 of the Directive;
7. As I shall explain in due course, Ireland does not deny that it has failed correctly to transpose Articles 2(3), 5 and 7 of the Directive. The allegations which I propose to consider are those concerning the mea- sures . by which Ireland has exercised the (g) to transpose the Directive within the option — available to Member States period prescribed in Article 12 thereof. under Article 4(2) of the Directive — of establishing the criteria and thresholds necessary to determine which of the pro- jects of the classes (or categories) listed in Annex II are to be subject, pursuant to Articles 5 to 10, to a prior assessment of their environmental impact. According to the Commission, in adopting the measures 5. Following the adoption of the reasoned in question Ireland exceeded its discretion opinion, there was an exchange of corre- under the Directive. spondence between Ireland and the Com- mission. By letter of 20 August 1993 Ire- land disputed part of the reasoned opinion; under cover of a letter of 7 December 1994, it sent a copy of the Local Govern- ment Regulations 1994; under cover of a 8. Those allegations essentially concern letter of 7 May 1996, it sent a copy of S.I. only three classes of project: use of uncul-
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tivated land or semi-natural areas for instrument and consistent with the aims intensive agricultural purposes; initial and rules of the Directive, for the prior afforestation or land reclamation; and assessment of under-threshold projects. extraction of peat. As grounds for its submission that the thresholds set by the Irish authorities infringe the Directive, the Commission makes a number of general points regarding all three classes of project to be considered by the Court. It then puts forward the arguments on the basis of which the infringements imputed to Ireland should be considered to be fully borne out Likewise, the Irish authorities did not take in respect of the separate grounds of action. due account of the way in which projects of the classes at issue may, because of their progressive effects over time (hereinafter 'incremental effects'), have a significant impact on the environment even though they do not exceed the thresholds set. Moreover, where various interested parties undertake a number of separate projects, none of which exceeds the thresholds, but which are carried out at the same time and in adjoining areas, their cumulative or Those general points may be briefly sum- incremental effects may cause environmen- marised as follows. tal damage and should not therefore be exempted from prior assessment under the Directive.
9. The Commission maintains that Ireland 10. Ireland contends that none of the failed, in setting the thresholds, to draw Commission's arguments has any basis in any distinction between areas which are of the provisions of the Directive governing importance and value for nature conserva- thresholds, or in the Court's interpretation tion and areas which are not; it disregarded of those provisions. Moreover, the Com- the fact that areas where nature conserva- mission has failed to show that the thresh- tion is important (because of their archae- old set for the classes of project at issue has ological or geomorphological interest, or in practice resulted in damage to the other environmental values) are often small environment consistent with some of the in relation to the physical area over which grounds of action. In particular, the argu- projects may extend in view of the thresh- ment founded on the possible cumulative olds set, even failing to take into account and incremental effects of projects which the absence of other suitable mechanisms in do not exceed the threshold should be Ireland, formally established by statutory regarded as inadmissible.
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The objection as to admissibility raised by ducted by the Commission and still under Ireland is a preliminary issue with respect way. to certain grounds of action and should be examined immediately.
12. In response, the Commission claims that it referred to the problem of cumula- tive and incremental effects with the sole and transparent aim of elucidating and developing the argument set out in the reasoned opinion to the effect that the Objection as to the admissibility of certain thresholds system adopted by Ireland incor- pleas and the related evidence rectly transposes the Directive precisely because Ireland neglected to evaluate, not only the size-capacity factor, but also other characteristics of projects; the problem of cumulative and incremental effects should therefore be viewed in relation to that of sensitivity of location, that is to say, of the location of projects in areas of potential significance in terms of environmental 11. Ireland submits that the Commission impact, a point already raised by the did not raise the above objection either Commission during the pre-litigation pro- during the administrative procedure or in cedure. the reasoned opinion. Accordingly, it con- stitutes a new plea and is therefore inad- missible, the Court having consistently held that, in proceedings against a Member State under Article 169 of the Treaty, the Commission may not raise before the Court pleas other than those relied on during the pre-litigation procedure. Ireland also main- 13. As regards Ireland's contention that tains that the evidence produced by the certain evidence is inadmissible, the Com- Commission in relation to the alleged mission explains that it had produced environmental impact of the cumulative factual examples of the practical repercus- and incremental effects of projects — argu- sions of Ireland's failure to fulfil its obliga- ments which, in Ireland's view, the Com- tions in the matter of thresholds. Moreover, mission has introduced in order to raise the information produced is, in part at new pleas before the Court — is also least, a matter of public record and is inadmissible. In gathering that evidence, associated only incidentally with informa- the Commission has relied largely, if not tion culled from other investigations pend- exclusively, on complaints submitted to it ing before the Commission, which lie out- by individuals, to which it did not refer in side the scope of these proceedings, and, in the reasoned opinion and which are the any event, available independently of such subject of separate investigations con- investigations, comprising established facts
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of which the Irish authorities are them- application and, accordingly, Ireland was selves aware and with which they were in a not deprived of the opportunity at the pre- position to take issue, in defence of their litigation stage to defend itself effectively. 2 own standpoint, in the course of the Such evidence may properly be allowed, administrative procedure. therefore, in proceedings before the Court, pursuant to Articles 40 and 42 of the Rules of Procedure.
Substance of the pleas. Preliminary obser- 14. I am inclined to agree with the Com- vations concerning the limits placed by the mission. Its argument concerning cumula- Directive on the discretionary power to set tion and incremental effects is unquestion- the thresholds at issue ably related to its complaint in the reasoned opinion, first raised during the pre-litiga- tion procedure, that the thresholds are inconsistent with the need to take into account the location of projects in areas which are sensitive but exempted from impact evaluation. Ireland's contention in 15. Before considering the merits, I should its rejoinder that, as a matter of logic, the like to make some preliminary remarks problem of cumulative and incremental effects arises independently of sensitivity of location, or the nature and size of the 2 — See the legal arguments set out in the Opinion of Advocate project, has no bearing on the complaint's General Cosmas of 26 November 1996 in Case C-157/94 Commission v Netherlands [1997] ECR I-5699: 'As the admissibility. In my view, it in no way Court has repeatedly observed, the purpose of the pre- detracts from the fact that the Commission litigation procedure is to give the Member State concerned an opportunity to comply with its obligations under views the consequences of the cumulative Community law and to avail itself of its right to defend itself against the complaints made by the Commission. and incremental development of projects Therefore the reasoned opinion with which that procedure exclusively in relation to their possible concludes must determine as clearly and specifically as possible the subject-matter of the dispute, that is to say, it impact on areas which are environmentally must contain all the particulars necessary to enable the Member State concerned to understand the factual and the sensitive. The facts relied on in that regard legal basis of the Commission's allegation that the State in by the Commission constitute evidence in question has failed to fulfil its obligations. If the reasoned opinion satisfies those requirements, the Commission's support of the arguments set out in the application will be admissible even though the arguments it contains, both factual (relating to the facts constituting reasoned opinion, but neither alter nor the situation or the conduct seen by the Commission as involving a failure by the defendant State to fulfil its extend the subject-matter of the dispute as obligations) and legal (concerning the interpretation of the delimited in the pre-litigation procedure: provisions of Community law which the Commission regards as having been infringed), may have been enhanced the substance of the infringement alleged by comparison with the arguments in the reasoned opinion, provided that such enhancement does not conceal an against Ireland, both in law and in fact, is alteration or extension to the legal and factual basis of the the same in the reasoned opinion as in the case as crystallised in the reasoned opinion.'
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concerning the nature of the test which the than Article 3: whenever impact assess- Court may apply. ment is carried out, it is necessary to identify and assess in each individual case the direct and indirect effects of a project on a number of factors which collectively constitute the 'environment' to be protected (human beings, fauna and flora, soil, water and the landscape, and their interaction, Yet again, the problem before the Court material assets and cultural heritage). concerns the limits to which Member States are subject when setting thresholds pur- suant to Article 4(2). In support of their respective arguments, both the Commission and Ireland have relied on the case-law clarifying the wording of that provision. The Court has consistently held that the choices which Article 4(2) leaves to Mem- ber States are discretionary but nevertheless subject to the limitations set by Arti- cle 2(1), which provides as follows: 'Mem- ber States shall adopt all measures neces- sary to ensure that, before consent is given, projects likely to have significant effects on the environment by virtue inter alia of their nature, size or location are made subject to 17. The Court has considered 'absolute an assessment with regard to their effects.' thresholds', that is to say, those which have been definitively established within a single class of projects corresponding, the Court has stated, not to the large groups desig- nated numerically but to the related sub- headings which are alphabetically listed. 3 A threshold of that type marks an auto- matic cut-off point. Projects which exceed 16. In my view, that requirement is of the level set are subject to prior assessment fundamental importance for the correct and authorisation. The others are not. It application and transposition of the Direc- was this effect — precluding as it does tive as a whole. It manifestly reflects the verification in the case of below-threshold political aim of preventing ecological projects — on which the Court focused, damage (see the seventh recital in the and in Kraaijeveld it laid down a test for preamble) and therefore lays down a gen- determining whether a State has exceeded eral obligation to carry out a timely and its discretion in that regard. The Court appropriate assessment which must precede affirmed that Article 4(2) entails the need authorisation of any of the projects, public to take into account, not the characteristics or private, envisaged by the Community of a single project, but the characteristics as legislation in point. Since Article 2(1) plays a whole of projects planned which fall a pivotal role in the Directive's structure, it must be read in close conjunction, not only with Article 4(2), but with many other 3 — See Case C-133/94 Commission v Belgium [1996] ECR provisions as well. We need look no further I-2323 and Case C-72/95 Kraaijeveld [19961 ECR I-5403.
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within the category under consideration. projects listed in Annex II subject to the That said, the Court established that the prior assessment procedure provided for by threshold may not be fixed at a level such the Directive if the characteristics of pro- that, in practice, all projects of the same jects belonging to those classes so require. class and nature are exempted in advance Article 2(1) expressly identifies which char- from impact assessment. acteristics are to be taken into account: primarily, the nature and size of the project, and its location. The latter is the one most closely connected with the present case.
The Court went on to state in Kraaijeveld that such a measure falls within the limits of the discretion only if, when viewed as a whole, all the projects exempted may be regarded as unlikely to have a significant impact on the environment.
19. The Directive has thus categorised 18. However, the question arises whether projects by class and by characteristics. in the present case that is the only restric- These are parameters or reference criteria tion to which Member States are subject which the national legislature must respect under Article 2(1) in view of the underlying when transposing the Directive. What aim of taking preventive measures to pro- implications does this have for the present tect the environment. I do not think so. case? Prior assessment is a general obliga- According to the test laid down by the tion under a rule which is both binding and Court in Kraaijeveld and in the other endowed with direct effect. 4The fact that judgments referred to therein, the key is an assessment must be carried out when the to evaluate threshold levels on the basis of characteristics of projects as defined in the exclusory effect they may have with Article 2(1) so require means that this is regard to the prior assessment of an entire an obligation, one might say, as to the category of projects. No reference class result to be achieved, which is binding on may be exempted a priori from impact the Member States, whatever methods they assessment. The classes are predetermined may have chosen to implement Arti- by the Directive and listed in either Annex I cle 4(2). To put it more clearly, for present or Annex II, according to whether the purposes: if the preferred mechanism is the projects envisaged therein (see the sixth threshold system, the Member States must and seventh recitals) — which are in any take all measures necessary when adopting event presumed to be significant in terms of it to ensure that impact assessment is environmental impact — are subject to the carried out whenever a project exhibits, assessment procedure governed by Arti- together with the other characteristics, that cles 5 to 10 directly (Annex I), or indirectly of being located in a sensitive area, and is (Annex II), through the choices left to Member States, such as the setting of thresholds. Member States may make the 4 — See Kraaijeveld (cited in footnote 3), paragraph 43.
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likely to have a significant impact on the the environment, it is inherently more environment. limited and less secure than supervision on a case-by-case basis, which is precisely why the 'margin' — in the words of the Court — of discretion left to Member States must be assessed by reference to specific standards. Admittedly, in Kraaije- veld, the Court rejected the Commission's argument that the setting of a threshold did 20. Moreover, as the Court observed in not relieve the State in question of the Kraaijeveld, there are certain standards obligation to determine whether each pro- which must always be met if thresholds ject met the criteria laid down in Arti- are to be justified. There is more than one cle 2(1). 5 The Court pointed out that reason for this. By operation of Arti- Article 4(2) expressly permits the setting cle 2(1), national authorities do not enjoy of thresholds and there is no reason why, a broader discretion if they opt for thresh- once the Member State concerned has olds than if they use other methods of chosen that option, each project should transposition available to them under Arti- still be subject to individual assessment on cle 4(2). There are indeed other options the basis of the criteria laid down in open to them provided, of course, that the Article 2. That is the clear and inescapable obligation as to the result to be achieved, conclusion. If, however, a threshold has not laid down by Article 2(1), is not thereby been set for the class of projects at issue (or circumvented or breached. Let us consider, if a threshold has been set, but is incon- for example, the case where a Member sistent with the Directive), the obligation State decides that it need not set the under Article 2(1) to determine in the case threshold at a level which makes sufficient of each individual project whether or not, allowance for sensitivity of location, in the light of its particular characteristics, because that would be either technically it must undergo assessment, arises anew. difficult or impracticable for some other Advocate General Mischo made this clear reason. The State in question may make in his Opinion of 12 March 1998. 6 provision for the areas most at risk of environmental damage by means of specific projects subject to impact assessment, waiving the threshold in such cases and arranging for another, more suitable, method of prior verification for the projects affected.
22. The approach adopted by Advocate General Mischo is vindicated by the new 21. Besides, the threshold is an abstract and general mechanism which by its nature sets aside all projects below the prescribed level 5 — See paragraph 49 of Kraaijeveld. as irrelevant for the purposes of impact 6 — See point 57 of the Opinion of Advocate General Mischo of 12 March 1998 in Case C-301/95 Commission v Germany assessment. As a mechanism for protecting [1998] ECR I-6135.
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version of Article 4(2) in Directive 97/11/ the theoretical and the practical level — EC, 7which replaces Directive 85/337/EEC. which is to identify, for each class of According to the new wording of that project, which projects should be subject provision, the Member States are to deter- to impact assessment and which should mine through a case-by-case examination not. Its effect, however, is to exempt a or by means of thresholds or criteria, or by priori virtually the entire class to which the both procedures together, whether any projects at issue belong. In the present case, project listed in Annex II should be made however, the question is not whether but subject to an assessment in accordance with how the threshold mechanism distinguishes Articles 5 to 10. The abstract thresholds the projects which are significant in terms mechanism and in concreto verification are of environmental impact from the others deemed to be equivalent and may even be within the same class. That problem, too, combined. Limited discretion is conferred concerns the discretionary power enjoyed here, as is also true of the test to be applied by the Member States and must be taken to the facts at issue. The version of fully into account when it comes to defin- Article 2(1) set out in Directive 97/11/EC ing the correct exercise of that power. I is substantially the same as in Directive have already pointed this out. Let me stress 85/337/EEC. Where a threshold is set, it that point, but with a different emphasis: if displaces the requirement, which would the threshold is adopted in breach of the otherwise apply, that each individual pro- criteria laid down in Article 2(1), the rules ject must be assessed. This confirms that, applying to projects (and to the related according to both versions of the legisla- 'developers', pursuant to Article 1(2) of the tion, thresholds may not be set which are at Directive) will, in my view, be tainted by variance with the aims of specific assess- unlawful discrimination, according to whe- ment or in disregard of any of the char- ther prior assessment is excluded or per- acteristics on the basis of which Article 2 mitted. For the purposes of prior assess- provides that impact assessments should be ment, the Directive in principle treats all carried out. the projects envisaged therein in the same way: Member States may at their discretion use thresholds (or similar mechanisms) in order to distinguish between projects only if they are consistent with the wording and purpose of Article 2(1).
23. If that requirement is not satisfied, the exclusory effect of the threshold will entail a breach of the criteria laid down in Article 2(1): the Member State will then have exceeded the limits of its discretion, as when operation of the threshold in practice exempts an entire class of projects from prior assessment. That is, as it were, an 24. How, then, is justification best mea- 'isolated' event, because the threshold ulti- sured in the present case? The question to mately defeats its own purpose — at both ask is whether or not the threshold mechan- ism, as devised, operates in such a way that the Directive is not complied with, an 7 _ Council Directive 97/11/EC of 3 March 1997 amending outcome which could have been avoided Directive 85/337/EEC on the assessment of the effects of through the use of other methods available certain public and private projects on the environment (OJ 1997 L 73, p. 5). owing to the discretion enjoyed by the
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Member States, provided, of course, that sary to comply with the obligation of prior they are consistent with Article 2(1). In the assessment; that obligation is laid down in following analysis of the separate grounds respect of projects which are likely to have of action, that is the test that I propose to a significant environmental impact and apply. 8 those, in the Commission's view, are the projects which concern 'sensitive' areas within the meaning considered above. If this is the thrust of the pleas under examination — and, in my view, it is — the only evidence that the Commission may
25. Now that the problem has been defined be required to produce is evidence to show in those terms, it is crucial in the context of that there are areas, identified by that these preliminary remarks to make an institution, in which the execution of the additional point regarding the matter of projects at issue may, in the light of their evidence, which is pertinent to all the issues characteristics, have adverse repercussions raised in this dispute. Is the Commission on the environment. It is not necessary, under an obligation to produce firm evi- however, to show that the impact envisaged dence that the environmental heritage has by the Directive as merely potential for the in fact been significantly damaged as a purposes of assessing its effect has actually consequence of the defendant State having occurred. Where the Commission provides set and applied thresholds exempting pro- such evidence as well, this would, if any- jects from impact assessment at the level thing, serve to confirm the assumption that chosen by it? there are areas below the threshold in dispute which are exposed to the risk of considerable environmental damage, in which the activities of the class considered should, because of their likely effects, have been subject to prior assessment.
26. As I mentioned above, Ireland contends that the Commission is under such an obligation. The most important point made by the Commission in response is the following: the proceedings which it has initiated concern the conformity of the Irish measures with the Directive, and the failure imputed to the defendant State is that of Projects for the use of uncultivated land or not having adopted the provisions neces- semi-natural areas for intensive agricultural purposes (Annex II, point 1(b)) 8 — In a sense, the Kraaijeveld test can be applied in the present
case. The Court devised a 'test' of 'last resort', so to speak, for use when the threshold is unlawful because it exempts an entire class of projects from impact assessment: the thresh- old may still be justified if the exempted projects, viewed as a whole, are unlikely to have a significant impact on the environment. In the present case, on the other hand, the question is whether the threshold is unlawful because it was 27. The threshold for the above class of set in disregard of the criterion of the project's location: the projects is laid down in Article 24 of the last-resort test of its justification is therefore satisfied if, on an overall appraisal of the characteristics of the exempted First Schedule, Part II, 1(a) of S.I_ No 349 projects, it transpires that none of them is located in a sensitive area, which would have rendered them subject to of 1989. That statutory provision provides impact assessment. for an environmental impact assessment
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(EIA) of certain areas to be carried out in listing as Natural Heritage Areas has been respect of projects for the use of unculti- proposed. vated land or semi-natural areas for inten- sive agricultural purposes, where the area concerned exceeds 100 hectares. The threshold was set at that level by virtue of Article 24 of the First Schedule, in con- junction with other provisions concerning land reclamation.
29. Ireland counters that those pleas fail to take into consideration, as they should, the entire class of projects at issue. The Com- mission has essentially confined its argu- The Commission submits essentially that ments to the land reclamation sector. As for operations have been carried out in areas the points concerning the semi-natural smaller than 100 hectares which may areas set aside for grazing, the Commission damage nature conservation and which has not even identified the geographical should not therefore have been exempted area referred to in its application, nor from impact assessment. It cited the case of demonstrated that the alleged conversion the Burren, County Clare, where the cumu- to intensive agriculture took place in areas lative effects of the operations threaten to smaller than 100 hectares and thus not alter or to destroy a very fine and extensive subject to prior assessment. There is no limestone pavement and the rare plants evidence in any of these cases to show that which grow there. The area in question is action has in fact been taken which has also characterised by important archaeolo- deleterious effects for nature conservation. gical remains. Ireland goes on to argue, striking a radical note, that the phrase 'intensive agricultural purposes' in Annex II, point 1(b), is not defined to a sufficient extent in the Direc- tive, contrary to the principle of legal certainty. Consequently, Member States are entitled to regard the provision on which the Commission relies as non-exis- tent. Furthermore, sheep grazing is outside 28. The Commission also contests the the scope of the Directive, however the exemption from impact assessment of notion of intensive agriculture is construed. approximately 60 000 hectares of semi- Grazing does not involve any interference natural areas set aside as pasture (and in with the natural surroundings or landscape particular for sheep farming) and thus which can or should form the basis of a converted to intensive agriculture. Over- project within the meaning of Article 1. grazing has caused and may yet bring about That follows both from the fact that farm- serious environmental damage to many ing is inherently a free and personal activity places which the Irish authorities them- and from the fact that farming in Ireland is selves acknowledge to be so important for traditionally practised according to the management· of the ecosystem that their system of commonage, which makes it
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practically unsuited to the arrangements over, it is not unreasonable, as Ireland introduced by the Directive. contends, to maintain that grazing should be subject to prior authorisation in accor- dance with the Directive; rather it is a simple and justifiable consequence of the protection which the Directive accords to the environment, and which applies to all forms of intensive agriculture and in gen- eral to the activities listed in the annexes, all of which are regarded as potentially damaging. Nor can the application of the Directive — which the defendant State is required to respect, and therefore to trans- 30. Let me deal with that last point first. pose accordingly — be hindered by the Ireland's rejoinder raises, above all, the special features of the Irish commonage problem of defining the category of inten- system in relation to grazing. The answer is sive agriculture (and related projects), clear. In this context, grazing belongs to the which Ireland maintains cannot include category of intensive agriculture. either sheep grazing or sheep farming. To my mind, however, the definition given in the list is clear enough to be correctly interpreted and applied in the present case. The uncultivated land and semi-natural areas referred to therein are those which undergo fundamental conversion in order to be used for intensive agricultural pur- poses. Grazing exploits the resources of the soil and therefore constitutes the kind of activity eligible for projects which should be subject to prior assessment (see Arti- cle 1(2)). There are intensive forms of grazing which can be measured, for exam- ple, in terms of stocking density and the number of sheep per hectare, as the Com- 31. The question therefore arises whether mission points out. It seems clear to me that or not the 100 hectare threshold set by Irish overgrazing may affect the environment legislation for that class of projects is just as much as any other activity listed consistent with the limitations to which under point 1(b) of Annex II, all the more the Member States' discretion in the matter so when the livestock is housed in fixed is subject. In order to answer that question, installations designed for that purpose, and I propose to apply the assessment criteria listed under other subheadings (see described above. The threshold in dispute point 1(e) and (f) of Annex II). Further- would be in breach of the lawful bounds of more, the Commission has raised pertinent discretion if it operated in such a way as to and serious objections to Ireland's defence exempt from impact assessment operations that the activity in question is not suited, or in semi-natural areas of less than 100 hec- even amenable, to the requirements and tares where the location of the project is technical aspects of the assessment proce- likely to have a significant impact on the dure provided for in the Directive. More- environment. The Commission alleges that
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overgrazing, wherever practised, exhibits into the existing authorisation procedures, the characteristics which, according to the or into other procedures or into procedures Directive, call for impact assessment. Ire- to be established in the legal systems of the land contests this on the abovementioned Member States. Accordingly, all these pro- grounds and also argues that in Ireland the cedures must be designed to achieve the environmental impact of grazing is mon- same aims as the Directive: the obligation itored under programmes established by of prior assessment, as laid down by Community regulations and designed to Article 2(1), is binding on the Member discourage intensive grazing, while the States when they introduce those other grant of financial assistance is subject to procedures into their respective legal sys- the condition that the farmers concerned tems, just as their discretion is limited in the must participate in the management of the cases provided for in Article 4(2). Rural Environmental Protection Schemes instituted by the defendant State.
The 'wide-scale monitoring' of the possible environmental impact of intensive grazing 32. The Commission has demonstrated (and, more generally, of the other activities that it received from the Irish authorities listed in the annexes) must, whatever the themselves, in the course of their exchange procedure laid down or the competent of correspondence (copies of which are in authority, bring about the result which is the case file), information showing that significant in the context of these proceed- approximately 60 000 hectares had been ings: it must therefore be organised on the ecologically damaged or endangered by basis of statutory provisions which are overgrazing. In my view, the Commission specifically designed to underpin recourse thereby provided sufficient evidence to to prior assessment, that is to say, which substantiate its ground of action (see prescribe such assessment where required point 26 above). by the Directive but excluded by the threshold.
33. How, then, to evaluate the measures for monitoring the environmental impact of 34. The Commission complains that there grazing which apply in Ireland indepen- is no guarantee that the desired result can dently of the threshold system at issue be achieved. Ireland has not put forward, it here ? To my mind, these must comply with seems to me, any argument to support the Article 2(2) of the Directive which provides opposite conclusion. From that I must infer that impact assessment may be integrated that the authorities responsible for mon-
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itoring environmental impact in under- The 100 hectare threshold applies to both threshold areas may exercise a broad types of operation. And it is in relation to discretion, which is in any event greater both that the Commission raises the ques- than that conferred on Member States by tion of the cumulative and incremental Article 4(2). effects of projects. Consonant with the order in which my arguments are deployed in this Opinion, I shall address that issue immediately.
If that is the position, then these other internal procedures, far from supplement- ing the Community legislative arrange- ments in point, run counter to them. In any event, Ireland cannot rely on the fact that it has provided for such procedures in order to rebut the Commission's allegation. 36. In bringing this problem to the Court's attention, the Commission refers once again to Ireland's obligation to determine the threshold in the light of the character- istics of projects. More specifically, how- ever, this entails the need to gauge how 35. The grounds for concluding that the projects should be evaluated in relation to 100 hectare threshold is not consistent with each other. That is the crucial aspect of this the Directive hold good, all the more so if plea. My analysis will focus on the project we turn to the points made by the Com- characteristics which have been mentioned mission concerning the Burren area. by the parties.
That the Burren is a sensitive area, as the Commission asserts, is attested to by the report issued in 1996 by the Heritage Council, entitled A Survey of Recent 37. The size of a project which by its nature Reclamations in the Burren. Numerous converts uncultivated land or semi-natural developments have taken place in the areas to other uses is calculated, for the Burren (breaking up and levelling of the purposes of setting a threshold, in terms of limestone pavement), a good many in areas surface area: 100 hectares. According to classified by the Irish authorities themselves the Commission, that threshold is not as Natural Heritage Areas. Various sites of correlated — or, at least, is not logically important historical and archaeological correlated, consistent with the proper exer- interest have been destroyed. As well as cise of a discretion — with the project's land reclamation, this case involves break- location, which had to be taken into ing up the soil, which is taken into account account in the case of areas particularly in the context of another ground of action. susceptible to the effects of operations of
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that particular kind. The Commission of whether one or more projects are argues that the threshold set is correlated involved. That is why the Commission to a sufficient extent with the factor of maintains that regard must be had both to sensitivity of location, only if it is applied incremental effects — those which develop having regard to: over time as a particular project pro- gresses — and to the effects which may follow from the cumulation of projects planned and carried out contempora- neously by separate developers in adjoining both areas which collectively encompass the 100 hectares set. Whenever a project is characterised by sensitivity of location, therefore, its prior assessment must be contemplated, subject always to verifica- (i) the individual projects planned for the tion that the area of land involved, if less area in question, which may affect than 100 hectares, exceeds that threshold relatively small areas, well below when considered in conjunction with other 100 hectares, as in the case of the areas affected by adjacent projects of the Burren, where deforestation or land same kind. conversion is fragmented, involving a number of operations and different developers;
39. Strictly speaking, this plea contests not the level of the threshold adopted in Ire- and land, but its application here, which the Commission regards as contrary to the Directive precisely because incremental and cumulative effects are not taken into account. The test is therefore: does it (ii) all the projects which, as a whole, follow from Articles 2(1) and 4(2), read affect the same area: in this context, together, that where Member States have the important factor for the purposes set thresholds, their application must be of prior assessment is therefore the full governed by the specific criterion argued impact of the operation to which the for by the Commission? projects, viewed individually or collec- tively, subject a section of the environ- ment which is recognised as deserving special protection.
40. Prior assessment concerns the charac- teristics of projects viewed in terms of their 38. The assessment procedure is, therefore, effects. The procedure is one of verification set in motion every time land development in concreto, and effects are therefore of the class and characteristics described attributed to the individual project. That affects more than 100 hectares, regardless does not mean, however, that the Directive
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excludes the cumulative and incremental tion is clearly an inevitable consequence of effects under consideration from the range the obligation to take into account even the of those that are relevant. Quite the con- indirect effects of projects on the environ- trary. Article 3 states in fact that prior ment when evaluating their characteristics. assessment is meant to identify the direct Both Directive 85/337 and the more recent and indirect effects of every project on all directive lay down that obligation in essen- the environmental factors. Incremental tially the same terms (cf. Articles 2 and 3 of effects obviously flow from the individual both directives). project, and are direct, because they are immediately linked to the progress of the operation planned by the developer. In my view, cumulative effects are also a proper subject for prior assessment, being attribu- table to the individual project, where the foreseeable impact of its characteristics is 42. I conclude, therefore, that the Commis- intensified by a conjunction of circum- sion's submissions are well founded: Ire- stances which are themselves relevant to land's failure to fulfil its obligations lies in environmental protection, such as the the fact that it did not base the threshold at aggregation of the individual project with issue on the necessary provisions enabling other projects in the sensitive area of its the incremental and cumulative effects of location. That makes it justifiable — and, projects to be taken into account in its in my view, necessary — to take cumulative application, having regard to the aforesaid effects into consideration when determin- conditions. It is therefore necessary for such ing whether the project exceeds the thresh- additional rules to be adopted, assuming old and should be subject to prior assess- Ireland maintains the threshold already set ment. and does not decide to transpose the Directive by other methods consistent with the proper exercise of its discretion.
41. Ireland contends in its defence that Member States were under no obligation to Annex II, point 1(d): initial afforestation take the cumulative effects of projects into where this may lead to adverse ecological account until the adoption of Directive changes and land reclamation for the 97/11. Directive 85/337, which applies to purposes of conversion to another type of the present case, is silent in that respect. land use However, the relevant annex to Directive 97/11 lists a series of selection criteria, focusing on the characteristics of projects and their potential impact. Cumulation is listed as one of the project characteristics. 43. Article 24, First Schedule, Part II, As in the case of the other application 1(c)(i) of S.I. No 349 of 1989 requires an criteria identified in the annex, the fact that impact assessment for initial afforestation the Directive specifically mentions cumula- where the surface area exceeds 200 hec-
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tares, and for the replacement of broadleaf subsidies had been granted to implement high forest by conifer species where the afforestation projects: in February 1994 in area in question exceeds 10 hectares. S.I. respect of an area of 76 hectares in Dun- No 101 of 1996 altered those thresholds, ragh Loughs and Pettigo Plateau; in providing in conjunction with other Irish December 1994 in respect of an area of statutory provisions that an impact assess- 44.1 hectares in Tullytresna Bog; and in ment must be carried out in the following March 1994 in respect of an area of cases: in respect of initial afforestation, 190 hectares in Tamur Bog. Those projects when the area involved — either on its own were not subjected to environmental or taken together with other adjacent impact assessment. According to the Com- wooded areas — has come over the pre- mission, the afforestation of blanket bog ceding three years to cover more than areas involves ploughing, drainage, the use 70 hectares. Where existing woods are to of fertilisers and radical changes of vegeta- be replaced by conifer species, the thresh- tion, operations which risk damaging or old is 10 hectares. Article 24, First Sche- even destroying the ecosystem of blanket dule, Part II, 2(c)(ii) of S.I. No 349 of 1989 bog. In support of its allegation, the sets, however, a threshold of 100 hectares Commission produced evidence showing for projects where the area is to be that in many areas, designated by the Irish reclaimed for conversion to another type authorities themselves as Natural Heritage of land use. Areas (Dunragh Loughs, Pettigo Plateau, Tullytresna Bog, Tamur Bog), unmoni- tored afforestation operations are under- way. The Commission quotes scientific studies attesting to the serious or even irreversible impact which such operations 44. The Commission takes issue with that may have on the areas in question, 9and legislation in so far as it leaves below the draws particular attention to the afforesta- threshold level, and thus exempts from tion project in Dunragh Loughs and Pettigo prior assessment, afforestation projects Plateau, areas of approximately 2 000 hec- planned for areas of blanket bog or for tares, which are considered to be of great areas near waterways. The Commission scientific interest because of the undis- also contests the threshold of 100 hectares turbed blanket bog. The Commission adds set for projects concerning areas which are that the importance of that area in envi- to be reclaimed for conversion to another ronmental terms has been recognised inter- type of land use. Those grounds of action nationally (900 hectares of the Pettigo should be examined separately. Plateau are covered by the 1986 Ramsar Convention), and in the context of Council Directive 79/409/EEC in relation to which Ireland itself designated 619.2 hectares of Pettigo Plateau as an area meriting special protection. Furthermore, Pettigo Plateau and Dunragh Loughs are mentioned in a contract concluded between the European (a) Afforestation of blanket bog areas Commission and the Irish National Parks
45. By letter of 6 May 1996 Ireland con- 9 — The Commission refers on this point to Stroud, Reeds and Others, Birds, Bogs and Forestry, the Peatlands of Caithness firmed to the Commission that various and Sutherland, Nature Conservancy Council.
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and Wildlife Service on 28 December 1995 Commission has failed to show that pro- in accordance with Council Regulation jects below the new threshold have a (EEC) No 1973/92, on the basis of which significant impact on the environment. In financial support was given for various any event, the afforestation projects plan- management and intervention programmes ned for Natural Heritage Areas are subject designed to protect and conserve the envi- to monitoring by the National Parks and ronment. In that connection, the Commis- Wildlife Service. The Habitat Regulations sion refers to the report entitled Survey of adopted by the Irish authorities protect the Breeding Birds at Pettigo Plateau, Country areas in question more effectively than Fermanagh, 10 which explains how the kind compulsory impact assessment: authorisa- of afforestation under consideration con- tion for afforestation is subject to compli- stitutes a serious threat to the protection of ance with environmental protection stan- the environment: conifer plantations have a dards equivalent to or higher than those fragmenting effect on the drainage system applied to projects which exceed the Irish of such areas, rendering them no longer statutory threshold. Moreover, afforesta- suitable as a natural habitat for various tion costs are so high that in practice the indigenous species of fauna (such as the operation requires financial assistance and Greenland white-fronted goose, the hen is not therefore exempt from the attendant harrier and the golden plover). Other supervision in the case of Natural Heritage species of bird and land mammal become Areas. more vulnerable with the arrival in the plantations of new predators.
46. Ireland contends that, following the Commission's reasoned opinion, the Law 47. In evaluating the Commission's sub- of 1 October 1996 reduced the impact missions, here as before, it should be noted assessment threshold from 200 hectares to that the applicant has focused on sensitive 70 hectares. Ireland has thus fulfilled its areas for which no prior assessment is obligations under that opinion and the required in respect of afforestation projects. The scientific reports and other evidence produced by the Commission show that the 10 — Rachel Bain and Clive Mellon, Summary Report, Survey of Breeding Birds at Pettigo Plateau, County Fermanagh, detrimental effects on the environment 1995, Royal Society for the Protection of Birds (RSPB). caused by the afforestation of peatlands is
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considerable. The point of law at issue here prior assessment applies whether projects is the same as was considered above in the are private or funded by the State. context of uncultivated land and semi- natural areas converted to intensive agri- culture. If the threshold exempts projects affecting sensitive areas from prior assess- ment, it cannot be concluded that in adopting that threshold the defendant State acted in the lawful exercise of its discretion. That is the position here. To my mind, therefore, the Commission's plea is well Nor is it pertinent to point out that the
founded. Admittedly, Ireland contends that Commission objected in its reasoned opi- it has made provision — in respect of nion to a 200 hectare threshold and that below-threshold projects as well — for the defendant State then reduced it to monitoring the impact of afforestation, 70 hectares. The Commission also consid- both generally by statute (S.I_ No 94/97 ers the lower threshold applied as from European Communities Regulations 1997) 1 October 1996 to be inappropriate and and through administrative procedures: the submits that, in setting that level, the Irish grant of subsidies for operations of that legislature took no account of the incre- kind is thus conditional upon strict verifi- mental effect, because it exempted from cation of their compatibility with the prior assessment projects which do not protection of the environment.
That con- exceed that level within three years; the tention is mostly argued on the basis of the developer concerned may, once the three practical need for financial assistance. Ire- years have elapsed, submit a new project land points out that afforestation was which will always remain exempt from initially managed by the State and only impact assessment provided it does not later by private enterprise, at times funded affect a surface area of more than 70 hec- by the European Community: and whoever tares. In calculating the overall effect of the pays the piper calls the tune. However, the project already executed and the new availability of subsidies, or any other project, the cumulative effect over time financial assistance granted by the Member should be borne in mind, as I explained State to developers on condition that they above (see points 40 and 41), and this respect environmental constraints is of no should always be taken into account when significance for the purposes of Article 1 of applying the threshold set, whatever its
the Directive: Article 1 makes arrange- level. ments for authorisation which is uncondi- tionally linked to the prior assessment of a project whenever it involves any of the matters listed in Annexes I and II. Prior assessment is incorporated in internal pro- cedures only in accordance with the condi- tions which I have described above (see point 33) and these cannot be waived by the Member States. In other words, the I shall pass over the allegation that Ireland incentive which drives the private devel- infringed Article 7 of the Directive in that it oper to seek funding has no bearing on the failed to fulfil its obligation to inform and controls required under the Directive: so consult the United Kingdom, which is an much so that the obligation to carry out interested party, given the fact that some projects, such as Pettigo Plateau, straddle
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the border. That is the subject of another 49. Both the Aquafor .report and other ground of action, which Ireland does not scientific studies attest, moreover, to the contest. damage caused by afforestation near water- ways. 1 1The plea is justified, however, in that the Commission has identified areas which are sensitive to the acidification of waters, such as the Counties of Galway, Wicklow, Donegal and Kerry. The scientific authority of the reports produced by the Commission and quoted in that regard provide clear evidence, to my mind, that afforestation should have been subject to prior assessment, whereas it is not: the threshold does not permit this, and there (b) Afforestation of areas near waterways are no adequate alternatives by which the environmental impact of the projects at issue can be monitored.
48. Using the reports on Aquafor and The Trophic Status of Lough Conn, the Com- mission has shown that afforestation in (c) Projects for land reclamation for the certain areas has a serious impact on the purposes of conversion to another type of environment because of the acidification land use and eutrophication of water. Ireland sub- mits that these reports should not be relied upon because the studies to which they relate were effected before the Directive 50. The arguments set out above must also came into force. There is no evidence, be applied to the evaluation of the 100 hec- therefore, to substantiate the Commission's tare threshold set in respect of projects for argument. Ireland's submission cannot be land reclamation for the purposes of con- upheld. It is useful to note that the two version to another type of land use, by studies merely define in scientific terms the application of Article 24, First Schedule, causal link between afforestation and the Part II, 2(c)(ii) of S.I. No 349 of 1989. The serious impact on the environment caused important case in this context is the Burren, by the acidification and eutrophication of examined earlier. Allow me to refer to my waters in certain parts of Ireland. They observations in that regard (see point 35 make an important contribution to the Court's analysis, not because they demon- strate the fact of environmental damage, 11 — See 'Evaluation of the Effects of Forestry on Surface-Water which is not an issue here (see point 26 Chemistry and Fishery Potential in Ireland', EOLAS Contract ER/90/76; N. Allott and Others, 'Stream Chem- above), but because they provide scientific istry and Forest Cover in Ten Small Western Irish guidance to the special nature of the areas Catchments' in Ecological Effects of Afforestation, Studies in the History and Ecology of Afforestation in Western in question and to the possible impact of Europe, 1993; N. Allott and M. Brennan, 'Impact of Afforestation on Inland Waters' in Water of Life, Dublin, afforestation projects located there. 1992.
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above). There are sound reasons for believ- Commission and the National Parks and ing that land reclamation represents no less Wildlife Service for the grant of a threat to the ecosystem than the conver- ECU 344 000 by way of funding for the sion of land for intensive agricultural preservation and protection of the peat- purposes. Projects involving that operation lands. in areas such as the Burren should therefore be subject to impact assessment, even if they affect an area of less than 100 hec- tares.
52. The threshold for peat extraction pro- jects was set at 50 hectares, as laid down in Article 24, First Schedule, Part II, 2(a) of S.I. No 349 of 1989. Ireland's defence — leaving aside the arguments disposed of Projects referred to in Annex II, point 2(a): above and put forward again in this extraction of peat connection — is essentially two-fold: (i) the Commission based its allegations almost exclusively on the exceptional case of Ballyduff-Clonfinane Bog, disregarding the test laid down in Kraaijeveld, which 51. Similar considerations weigh in favour requires account to be taken of the char- of upholding the next plea which concerns acteristics of all the projects of the class at the effects on the environment of projects issue, never of one project alone; and (ii) for the extraction of peat. Such operations the threshold was set at 50 hectares may constitute — according to the Com- because the Irish legislature wished to draw mission, and I see no reason to disagree — a distinction between the commercial one of the most serious threats to the exploitation of peat and the tradition of integrity of the environment, particularly in turf-cutting, practised for centuries in rural the case of the peatlands at issue. The Ireland, that is to say the hand- cutting of extraction of peat in boggy areas involves peat by an individual for his family needs. drainage. That in turn leads to the drying out of peat-forming vegetation. The low- ering of the water table causes shrinkage of the peat content of the bog; the slope of the bog becomes more acute, increasing the water run-off, and exacerbating the drying- out process. In that connection, the Com- mission cites the example of Ballyduff- 53. In my view, neither defence should be Clonfinane Bog in County Tipperary, upheld. As I have already explained (see which is examined in detail in Complaint point 24 above), the criterion of the loca- No P.95/4218. That site, which consists of tion of the project is disregarded whenever two separate bogs, forms a complex of the threshold effectively precludes impact 312 hectares and was designated a Natural assessment notwithstanding the serious Hertitage Area in 1995. On 28 December potential impact of the operation in ques- 1995 a contract was concluded between the tion, in view of its location. The number of
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projects affected by the threshold's exclu- above), therefore, I would conclude that sory effect is irrelevant, in the light of the the threshold set gives rise to unjustified criterion relied upon by the Commission. discrimination between projects of the class at issue (and between the respective devel- opers). It should also be borne in mind that Irish legislation treats peat-cutting differ- ently from analogous extraction operations (the quarrying of stone, gravel, sand or shale), listed elsewhere in Annex II, for which it has set a much lower threshold 54. Nor does it seem to me that Ireland's (5 hectares). It has yet to be shown that approach can be validated by the argument projects included in those other classes are that above-threshold operations are com- likely to have a greater impact than peat mercial whereas below-threshold opera- extraction in sensitive areas; therefore the tions are manual and traditional, hence rules laid down by the Irish legislature in there is no justification for subjecting them respect of the various extraction operations to impact assessment. In its reply, 12 the listed under separate headings in Annex II Commission maintained that the justifica- may well give rise to an unjustified differ- tion for that distinction is unsustainable ence of treatment as well, all such opera- because turf-cutting by hand has largely tions being relevant in terms of their given way to mechanical harvesting, with potential impact on the environment. Con- the result that small and medium-scale sequently, in my view, this ground of action commercial exploitation is now wide- is also well founded. spread.
55. The only relevant point here is the possible impact of peat extraction on the areas in question. It should be borne in Infringement of Articles 2(3), 5 and 7 of mind that, as the Commission points out, the Directive peat extraction may provoke irreversible changes in the ecosystem of the bogs. The Commission acknowledges that turf cutting by hand, hallowed in Irish tradition, 13 falls outside the scope of the Directive. It is the commercial exploitation of areas of less 56. S.I. No 349 of 1989 makes provision than 50 hectares, therefore, which ought to for the competent minister to exempt a have been taken into consideration and, so project from assessment wherever this is far as we can tell, it has not. On application warranted by exceptional circumstances. of the criterion set out above (see point 23 The Commission maintains that this arrangement is not consistent with Arti- cle 2 of the Directive because: (a) the 12 — See especially paragraph 19 of the Commission's reply. 13 — And even in Irish literature: see paragraph 106 of Ireland's minister is not required to determine whe- defence. ther another form of assessment is appro-
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priate or whether the information collected through measures in the course of adop- should be made available to the public; and tion. (b) the minister is not required to inform the Commission.
57. Article 2 of S.I. No 349 of 1989 pro- 60. Therefore, those grounds of action vides simply that an impact study may must also be upheld. Ireland has failed to contain information. The Commission fulfil its obligation to transpose Articles 2, points out that the Irish legislation does 5 and 7 of the Directive into national law not ensure, in accordance with Article 5 of within the period prescribed by the Com- the Directive, that developers provide in an mission in its reasoned opinion. appropriate form the information specified in Annex III thereto, in the case of projects which must be subjected to impact assess- ment.
61. To sum up: the present dispute raises the problem, on which the Court's ruling 58. The Commission also points out that will undoubtedly shed light, of determining Article 17 of S.I. No 25 of 1990 fails to how the choice of threshold — the 'abso- provide a suitable mechanism transposing lute' threshold (see point 17 above) — fits into national law the rules governing the in with the methods open to the Member Member States' obligation to transmit the States, pursuant to Articles 2(1) and 4(2) information collected under Article 5 of the read together, of transposing the Directive Directive to another Member State, where into national law. As I have indicated, a project is likely to have significant effects Ireland will be able to remedy the situation on that State's environment and where it by adjusting its threshold system or by requests the information pursuant to Arti- adopting other measures within its discre- cle 7 of the Directive. tion. However, the discretion enjoyed by the Member States must always and only be exercised within the limits set by the Court in previous judgments and which it is called upon to define in the present case. In many respects, the Directive in question is comparable to a regulation in view of the 59. Ireland does not deny that it has failed direct effect of its key provision (Arti- correctly to transpose Articles 2, 5 and 7 of cle 2(1)) and the exhaustive nature of its the Directive into national law. It has stated legislative content; moreover, its approach its intention to clarify its legislation to the protection of the environment
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embraces the entire range of aims contem- exercise of the discretion conferred on it. plated, including nature conservation. As Furthermore, as the Commission acknowl- Ireland points out in its defence, nature edges, aside from the points at issue in these conservation is also subject to other Com- proceedings, Ireland has not failed to munity legislation, but in my view such transpose the Directive correctly into its rules in no way prevent a Member State national law. Should the Court decide that, from fulfilling its obligations under Arti- for the reasons set out above, Ireland has cle 2(1), the touchstone for the Court's failed to fulfil its obligations, the thresholds analysis of this case. at issue need not necessarily be reduced — nor indeed has the Commission specified a particular level to which they ought to be reduced — as if that were the only way to pass, like Alice in Wonderland, through a That said, we must not forget that the magic door. If the plea is upheld, however, Commission has confined itself to alleging the Irish legislature will in any event be that Ireland has failed to comply with the required to make provision, generally and specific, albeit fundamental, criterion of in such a way as to meet the requirements sensitivity of location, and has quoted of legal certainty, for situations where cases — or rather, examples — which projects are located in sensitive areas, in arguably show that its general criticism is order to ensure that they are subject to well founded. The question how the Irish prior assessment in full and proper confor- legal system may best be adjusted to take mity with the Directive. This holds true adequate account of that criterion is a whatever method is chosen in order to matter for Ireland (as for any other Mem- implement the provisions of Article 4(2). ber State) in the balanced and lawful
Conclusion
In the light of the foregoing, I suggest that the Court rule as follows :
(1) By failing to adopt all the measures necessary to ensure the correct transposition of Article 4(2) into national law in respect of the projects listed under point 1(b) and (d), and point 2(a) of Annex II to Directive 85/337/EEC and by failing, in part, to transpose Articles 2(3), 5 and 7 of that Directive
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into national law, Ireland has not fulfilled its obligations under Article 12 thereof or under Article 169 of the EC Treaty.
(2) Ireland is ordered to pay the costs.
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