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UNUnited Nations Economic Commission for Europe

Protocol on Strategic Environmental Assessment (SEA)

Implementation of Directive 2001/42 on the Assessment of the Effects of Certain Plans and Programmes on the Environment (the 'EC Guide')


7. CONSULTATION

Table of Contents

9. RELATION WITH OTHER EC LEGISLATION

8. MONITORING

8.1. Article 10 extends Member States' duties beyond the planning phase to the implementation phase and lays down the obligation to monitor the significant environmental effects of the implementation of plans and programmes. Monitoring is an important element of the Directive since it enables the results of the environmental assessment to be compared with the environmental effects which in fact occur.

8.2. The Directive does not prescribe how the significant environmental effects are to be monitored, for example, the bodies responsible for monitoring, the time and frequency of monitoring, or the methods to be used. Although monitoring activities are widespread across the EU, the information gathered is not always readily available or in comparable formats, even within the same administration. Member States may wish to consider whether any legal or administrative measures are needed not merely to ensure in accordance with the Directive that monitoring takes place but also to go further and enable data to be accessed and shared when appropriate, so that the obligations of Article 10 can be discharged efficiently.

Article 10(1)

Member States shall monitor the significant environmental effects of the implementation of plans and programmes in order, inter alia, to identify at an early stage unforeseen adverse effects, and to be able to undertake appropriate remedial action.

8.3. Article 10 establishes that monitoring of the significant environmental effects of plans and programmes covered by the Directive is an obligation. When a plan or programme is adopted, the authorities referred to under Article 6(3), the public and any Member State consulted under Article 7 must be informed about 'the measures decided concerning monitoring in accordance with Article 10' (Article 9(1)(c)).

8.4. The Directive does not define the meaning of 'monitor'. Monitoring can, however, be generally described as an activity of following the development of the parameters of concern in magnitude, time and space. In the context of Article 10 and its references to unforeseen adverse effects and remedial action, monitoring may also be a means of verifying the information in the environmental report. Article 10 does not contain any technical requirements about the methods to be used for monitoring. The methods chosen should be those which are available and best fitted in each case to seeing whether the assumptions made in the environmental assessment correspond with the environmental effects which occur when the plan or programme is implemented, and to identifying at an early stage unforeseen adverse effects resulting from the implementation of the plan or programme. It is clear that monitoring is embedded in the context of the environmental assessment and does not require scientific research activities. Also the character (e.g. quantitative or qualitative) and detail of the environmental information necessary for monitoring depend on the character and detail of the plan or programme and its predicted environmental effects.

8.5. If monitoring can be satisfactorily integrated in the regular planning cycle, it may not be necessary to establish a separate procedural step for carrying it out. Monitoring may coincide for example with the regular revision of a plan or programme, depending on which effects are being monitored and upon the length of intervals between revisions.

8.6. Monitoring has to cover the significant environmental effects. These cover in principle all kinds of effects, including positive, adverse, foreseen and unforeseen [19] ones. They may usually be the effects described in the environmental report (in accordance with Article 5 and Annex I(f)) and so will often be focused on the information that 'may reasonably be required taking into account the contents and level of detail in the plan or programme and its stage in the decision-making process' (Article 5(2)). It is possible that monitoring of other effects may sometimes be justified (for example, effects which were not foreseen when the plan or programme was drawn up).

8.7. The other elements of Annex I will not usually be relevant in implementing the monitoring requirement but it may in some circumstances be convenient to link the results of monitoring with, for example, environmental problems, environmental protection objectives, or mitigation measures identified under paragraphs (d), (e), or (g) of Annex I. The Directive does not, however, contain a requirement to that effect.

8.8. Article 10 appears not necessarily to require that significant environmental effects are monitored directly. The Directive also allows them to be monitored indirectly through, for example, pressure factors or mitigation measures.

8.9. Implementation means not only the realisation of the projects envisaged in the plan or programme (including both their construction and operation) but also covers other activities (such as behavioural measures or management schemes) which form part of the plan or programme (or its implementation).

8.10. Article 10 requires the significant environmental effects of the implementation of all plans and programmes subject to the Directive to be monitored. It does not specify whether this has to be done for each plan or programme individually. In view of the flexibility of Article 10, one monitoring arrangement may cover several plans or programmes as long as sufficient information about the environmental effects of the individual plans or programmes is provided and the purposes and obligations of the Directive are fulfilled.

8.11. In some cases, the cumulative effects of different plans and programmes may be easier to identify when they are monitored together.

8.12. One of the purposes of monitoring identified in Article 10 is to identify unforeseen adverse effects. It is unlikely that a reasonably practicable monitoring scheme could be devised which, except by chance, would reveal completely unexpected effects (if any materialised) and that can hardly be the intention here. Even though unforeseen changes in the environment might be detected it may be difficult to attribute them to the implementation of the plan or programme. Unforeseen adverse effects is better interpreted as referring to shortcomings of the prognostic statements in the environmental report (e.g. regarding the predicted intensity of an environmental effect) or unforeseen effects resulting from changes of circumstances, which have led to certain assumptions in the environmental assessment being partly or wholly invalidated.

8.13. One purpose of monitoring is to enable the planning authority to undertake appropriate remedial action if monitoring reveals adverse effects on the environment that have not been considered in the environmental assessment. The Directive does not, however, necessarily require Member States to modify a plan or programme as a result of monitoring. This is consistent with the general approach of environmental assessment, which facilitates an informed decision, but does not create substantive environmental standards for plans or programmes. If, in the framework of their national legislation, Member States were considering remedial action, any relevant information received through such monitoring could naturally be of assistance.

8.14. If an adopted plan or programme is modified as a result of monitoring, this modification may again require an environmental assessment (if it meets the requirements of Article 2(a)) unless it is a minor modification and Member States do not determine that significant environmental effects are likely to occur (Article 3(3)). It is likely that plan modifications resulting from monitoring will serve to offset or mitigate adverse environmental effects. When deciding whether the modification of the plan has to undergo an environmental assessment relevant factors in deciding the significance of effects may include how far the environmental performance of the plan or programme will be improved and which environmental effects have already been subject to a comprehensive environmental assessment.

Article 10(2)

In order to comply with paragraph 1, existing monitoring arrangements may be used if appropriate, with a view to avoiding duplication of monitoring.

8.15. Article 10(2) helps clarify the obligations deriving from Article 10(1). Information on the effects of plans and programmes does not have to be collected specifically for this purpose, but other sources of information can be used. It also implies that there is no requirement to establish a new procedural step for the purpose of monitoring which is separate from the regular planning process, provided that process contains adequate monitoring arrangements. Monitoring can, for example, be integrated into the regular revision of the plan or programme. If no appropriate monitoring schemes exist Member States have to develop them.

8.16. The main challenge is to identify sources of information in different Member States that are a suitable basis for implementing the monitoring requirements and, if necessary, to adapt existing monitoring arrangements to the requirements of the Directive. Data collected under other EU legislation (e.g. Water Framework Directive 2000/60/EC, IPPC Directive 96/61/EC) may be used for monitoring in accordance with Article 10 provided that they are relevant for the respective plan or programme and its environmental effects.

Related Aspects and Provisions

8.17. Article 5 and Annex I(i) together require that the public is informed on the monitoring arrangements 'envisaged', and Article 9(1) requires the public to be informed of 'the measures decided concerning monitoring'. These provisions are discussed in paragraph 5.29 above. Information on the monitoring measures decided is subject not only to Article 9(1) but also to the provisions of Directive 2003/04/EC of the European Parliament and of the Council of 28th January 2003 on public access to environmental information.

8.18. When appropriate, the environmental assessment will also cover transboundary environmental effects (see Article 7 and also Annex II(2), 3rd indent). Consequently, transboundary environmental effects may also be subject to monitoring. Therefore, in case of plans and programmes which require transboundary consultation, any arrangements concluded under Article 7 may also address monitoring measures. An inspiration for such arrangements could be the provisions of Article 7 of the Espoo Convention.

8.19. Monitoring may assist in the area of quality control (Article 12(2)). If monitoring reveals that a certain effect is systematically overlooked or underestimated in the environmental assessments of a certain type of plan or programme, then monitoring can help to improve the quality of future environmental reports. Generally speaking, monitoring may provide information on the quality of the existing environmental report which may be used for the preparation of future environmental reports. In that regard, efficient monitoring can be regarded as a tool for quality control helping to fulfil the requirements of Article 12(2).

Notes

[19] See explanation of 'unforeseen' effects in paragraph 8.12.


7. CONSULTATION

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9. RELATION WITH OTHER EC LEGISLATION