and more broadly a part of the <strong>SEA</strong> ideology of improving strategic decision making.However, these changes have created a degree of tumult in local authority planning practicesand the role of SA and <strong>SEA</strong> are dependant upon the wider question of how environmentalpolicies and sustainability will be dealt with in the revised planning system.7.5 The expectations towards the introduction of <strong>SEA</strong> nationallyEstablishing the expectations towards the transposition of the EU directive 2001/42/EC tothe national legal framework is not clear-cut. The expectations may differ between thedifferent actors within the institutional system; between the national authorities, the plannersat different governmental levels, politicians and the legislators. The expectations can beexplicitly expressed in legislation, regulations and guidelines, or can be implicitly interpretedfrom those documents as well as official discussions leading to the legal introduction.In Sweden the main regulations on procedures and documents are given by theEnvironmental Code, but will be supplemented with specific regulations in the separatesector legislations and for spatial planning. The aims of the Swedish environmentalassessment process are incorporated in the overall objectives of the Environmental Code andare centred on the promotion of sustainable development and ‘healthy and soundenvironment’. The more specific purpose of the Environmental Assessment process isillustrated in chapter 6, which is to integrate environmental aspects in the plan or programmein order to promote sustainable development. Looking at the work carried out in relation tothe implementation of the directive into Swedish legislation, in the form of interim reportsfrom the committee set up for the revision of the Planning and Building Act that waslaunched in 2002 that the requirements of the directive shall be fulfilled. However theimplementation shall be integrated as far as possible to the existing framework and withminimum disruption and shall not exceed the directive’s minimum requirements.In Iceland the expectation of the directive as being an important tool in modernising theplanning system and contributing to the development of a new planning culture have beenexpressed by leading figures in the national planning administration. At a NordicEnvironmental Assessment conference in Reykjavík in 2003, an official at the Ministry of theEnvironment stressed the evolving legal context to which the <strong>SEA</strong> directive will beintroduced in Iceland, as well as the limited use of plans and programmes as policy tools. Thisview is also expressed by the director of the national Planning Agency, who attaches highexpectations to the implementation of the directive as a support for the modernization of theplanning system (Thors 2004). When the new act on environmental assessment of plans andprogrammes was presented for the Icelandic parliament in 2004, the chairman of theenvironmental committee stressed the importance of recognising the differences between thenew act of strategic environmental assessment and the existing legislation on environmentalimpact assessment of projects. He states “It is not the intention to lead to duplicate the work inconnection to EIA, nor to complicate administration or to make development difficult. On the contrary, thecommittee hopes that by considering in a systematic way the effects of development, the need for work and costswill be reduced at later stages. […] First and foremost the aims of the bill are that environmental viewpointswill be considered as early in the process as possible”. (Thórdarson 2005) 21 . The general findings ofthe environmental committee also stressed the importance of separating the EIA and <strong>SEA</strong>processes, as well as the importance of ensuring the public’s access to the informationpresented in the assessment report. In this respect, the importance of presenting theinformation in an easily understandable way is particularly stressed, as well as the opportunityfor other organisations and institutions to submit comments. In a report discussing the21 English translation: Hólmfrídur Bjarnadóttir106
preconditions for the introduction of the EC directive in Iceland; ‘Forsendur innleiðingartilskipunar Evrópusambandsins á Íslandi’ (Skipulagsstofnun 2003), published by the IcelandicPlanning Agency, the potential of <strong>SEA</strong> of <strong>SEA</strong> to make planning better equipped to promotesustainable development is highlighted. However, it is stressed that the planning environmentto which it is introduced limits the effects of the Environmental Assessment. One of theissues that are considered to increase the impacts of <strong>SEA</strong> to promote SD is that there is acomprehensive system of planning and operation plans in place with clear connections,horizontally as well as vertically, as well as between the different tiers and sectors. With theintroduction of the Planning and Building Legislation in 1998, the municipal plans becamethe fundamental planning instrument of the Icelandic planning system. On the other hand theformation of a planning strategy has not been distinct on the national or regional level, sincethere has not been a regional planning level in the country. However, there is visible anincreasing emphasis on planning and programming on the national level, as can e.g. be seen inlegislation on sector planning. Furthermore, there is an increasing consciousness of the needto coordinate planning strategies nationally, both horizontally between different programmingactors nationally, as well as (not less) vertically with regard to planning and programmingprocess with regard to environmental considerations, transparency and consultation. <strong>SEA</strong> ison the other hand not regarded to capable of creating connections between the differentsectors or administrative levels, if a comprehensive net of plans and programmes is not inplace.In England the expectations towards the directive in the context of spatial planning arenot easily interpreted, where the main objective of the introduction is to fulfil therequirements placed by the EU. The system of Environmental Appraisal has developed in theUK during a decade, where the instrument had taken different forms with regard to its scopeand role in the planning process, but thoroughly grounded in the ideas of sustainabledevelopment. Its statutory importance can be said to be highlighted as an example of animportant instrument in the national strategy for sustainable development, and integrated inthe Planning and Compulsory Purchase Act and in the guidance for the <strong>SEA</strong> implementationit is highlighted that the application of <strong>SEA</strong> to the planning process, can be integrated withthe existing process of SA.7.6 Analytical modelsLooking at the results from the review of the introduction of the <strong>SEA</strong> directive 2001/42/ECinto the national system with regard to three broader categories of implementation discussedby Emmelin and Lerman (2005), certain similarities can be identified. The categories arebased on the idea that the implementation of the EU directive could be classified into:• Minimalist, i.e. introducing <strong>SEA</strong> with the objective of implementing the directive in thespecific national context with minimum of disruption• Intentionalist, i.e. aligning national legislation with the intention of the directive• Environmentalist, i.e. use the directive as a lever to change national policy.The Swedish approach to implementing the requirements of the directive could be termed‘minimalist’ with the objective of implementing the directive in the national context withminimum disruption (Lerman and Emmelin 2005). In contrast, expectation levels have beenraised in Iceland that the directive can be used as a lever to change the national approach toplanning by strengthening the use of plans and programmes as policy tools (Thorgeirsson2003) and as a support in modernising the planning system (Thors 2004). With regard to the107
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- Page 127 and 128: Christoferson, I. (ed), (2001) Swed
- Page 129 and 130: Kørnøv, L. (1999) Integrating SEA
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- Page 133 and 134: European Union’s publicationsEC (
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