analytical framework above, this approach could be termed as environmentalist, i.e. there areexpectations among national actors that the introduction of the directive could be used as alever to change national policy, not only as a way to introduce environmental aspects, but tostrengthen the spatial planning system. Some of these changes will be included in the revisedPlanning Act, inter alia; a new national planning level will be created with the preparation of aNational Planning Policy. However, the legislation resulting from the discussions on <strong>SEA</strong>, the<strong>SEA</strong> Act adopted in 2006 closely follows the approach of the <strong>SEA</strong> directive and thus doesnot reflect this expectation of <strong>SEA</strong> as an innovative instrument of change. The Englishapproach is largely based on continuing to build upon tools that have been in development inthe UK over the last decade; i.e. sustainability appraisal. Sustainability takes a broaderapproach including both social and economic considerations on par with the environmentalconsiderations. It appears to be the ruling view, both in legal guidance, as well as academicliterature originating from the UK, that the existing requirements on EnvironmentalAppraisal are further developed than those of directive, with more ambitious goals andrequirements that have been developed on the basis of experience of application in the UKcontext. However, the application of Sustainability Appraisal at the local authority level hasreceived the criticism of being vague, and reviews have illustrated that the results have largelydependant upon the interest and ambition of the local authorities. With the introduction ofthe <strong>SEA</strong> directive certain aspects need to be more defined, i.e. new requirements onenvironmental baseline data, consulting the public and authorities during that assessment, andnot least, how the results are integrated into decision-making. Coincidentally, theimplementation of the directive takes place at the same time as fundamental changes areoccurring in the English town planning system and the move from the preparation of localplans at the local authority level, to the introduction of local development documents that willeffectively replace local plans, unitary development plans and structure plans.Sheate et al (2001) presented three models for environmental integration, i.e. the‘Constitutional/legislative model’, the ‘Process/strategy model’ and the ‘Ad-hoc institutionalmodel’, for analysing the findings from the three countries’ approaches for introducing the<strong>SEA</strong> directive to their national legislations. Furthermore Sheate et al presented models of<strong>SEA</strong> practice; ‘EIA inspired <strong>SEA</strong>s’, ‘policy analysis/appraisal inspired <strong>SEA</strong>’, ‘policyintegratory <strong>SEA</strong>’ and ‘Ad hoc mechanisms of environmental integration’. Applying themodels it becomes apparent that the experience of actual application include a mixture of thedifferent model of environmental integration and <strong>SEA</strong> practice.On the basis of those models, he following conclusions can be made:The Swedish approach of introducing <strong>SEA</strong> resembles largely the ‘Constitutional/legislativemodel’ in that it introduces minimum requirements for <strong>SEA</strong> in the existing environmentallegislations, i.e. the Environmental Code. Furthermore, the <strong>SEA</strong> requirements are introducedin the same chapter as the previous requirements on EIA, and the same authority isresponsible for preparing guidelines for the two processes, and resembles in that way one ofSheate four broad models of <strong>SEA</strong> practice (Sheate et al 2001) ‘EIA inspired <strong>SEA</strong>s’. However,the <strong>SEA</strong> introduction also involves other parties, most notably The National Board ofHousing, Building and Planning (Boverket) and the Planning and Building Act where theapproach could be argued to bear stronger resemblance to the ‘Process/Strategy Model’.The Icelandic approach to the <strong>SEA</strong> introduction also involves specific legal proceduresthat impose duties on public bodies (i.e. Constitutional/legislative model), but in the Icelandiccase the separation from EIA has been an explicit objective during the introduction of thedirective. Furthermore, the connection to the land use planning system has been strongduring the introduction of the directive, and the introduction of <strong>SEA</strong> in parallel to therevision of the Planning and Building Act has been an important influence, even to the extent108
that the directive has spurred the discussion on a new national planning level. Hence it can beclaimed fall into the category of the ‘Process/Strategy Model’ or the ‘policy analysis/appraisalinspired <strong>SEA</strong>’.In England the <strong>SEA</strong> requirements are introduced by a separate <strong>SEA</strong> regulation.However, the introduction of <strong>SEA</strong> is integrated in the institutional tools that existing for theplanning system and hence would closely resemble ‘policy appraisal inspired <strong>SEA</strong>’ accordingto the categories presented by Sheate et al (2001). However, meanwhile the <strong>SEA</strong> introductionis explicitly affected by an existing tool with similar objectives of integration, namely thesystem of sustainability appraisal that has been a regulatory requirement in England since1992 for local development plans and will be introduced to an existing practice ofsustainability appraisal. The reference to EIA and environmental protection is minimal in theEnglish approach. Applying the triple structure presented above, the transposition of thedirective in England assembles the minimalist approach, with the main objective of fulfillingthe EU requirements. At the same time, much of the intentions of the directive have in recentyears been implementing by the introduction of environmental appraisal as well as recentchanges in the spatial planning system. It could therefore be argued that the English style ofimplementation falls into the intentionalist category of implementation.In summary it can be claimed that the three countries studied have chosen differentframe of reference for the introduction of <strong>SEA</strong>, e.g. the framework provided by EIA, theland-use planning processes and the practice of sustainability appraisal.A comparative summary of the three countries’ introduction of the <strong>SEA</strong> directive ispresented below:109
- Page 1 and 2:
sea in the context of land-useplann
- Page 4 and 5:
Blekinge Institute of Technology Li
- Page 7:
AcknowledgementsThis thesis has dev
- Page 10 and 11:
CHAPTER 5 INTRODUCTION OF SEA TO TH
- Page 13:
PART I - Introduction to the resear
- Page 16 and 17:
In this research the introduction o
- Page 18 and 19:
my studies and work in the area as
- Page 20 and 21:
FIGURE 1.1. BASIC TYPES OF CASE-STU
- Page 22 and 23:
• Process/Strategy Model; i.e. co
- Page 25 and 26:
Chapter 2The SEA Directive 2001/42/
- Page 27 and 28:
was extended again to also encompas
- Page 29 and 30:
The plans and programmes referred t
- Page 31 and 32:
effects), with less attention given
- Page 33 and 34:
widespread voluntary application of
- Page 35 and 36:
assessment instruments such as Risk
- Page 37 and 38:
3.1.4 The origins of SEA and its re
- Page 39 and 40:
3.2 Relevance of planning theory fo
- Page 41 and 42:
development of its central ideas an
- Page 43 and 44:
aspects of environmental considerat
- Page 45 and 46:
FIGURE 3.2. SEA TOOLS IN RELATION T
- Page 47:
planning theory in respect of envir
- Page 51 and 52:
Chapter 4 Introduction of SEA to th
- Page 53 and 54:
to the ordinance (2005:356), the fo
- Page 55 and 56:
planning area and the 0-alternative
- Page 57 and 58:
4.4 Preparation work for SEA applic
- Page 59 and 60:
Housing and Planning has argued tha
- Page 61 and 62:
Municipal comprehensive plans (öve
- Page 63 and 64: 4.6.2 On-going legal revisionsOn-go
- Page 65 and 66: municipal comprehensive plans (25 p
- Page 67 and 68: A pilot study on impact assessment
- Page 69: despite the committee’s suggestio
- Page 72 and 73: esources, and the community, includ
- Page 74 and 75: There amongst it shall be decided w
- Page 76 and 77: Information made available in the r
- Page 78 and 79: Environmental assessment has been i
- Page 80 and 81: Level Authority Type ofplanningDesc
- Page 82 and 83: National initiatives for sustainabl
- Page 84 and 85: limited research that has been carr
- Page 86 and 87: equired by the SEA directive. Simil
- Page 88 and 89: - Setting the context and objective
- Page 90 and 91: Screening (the determination ifthe
- Page 92 and 93: assessment for the EU structural fu
- Page 94 and 95: Level Authority Type ofplanningDesc
- Page 96 and 97: experience of sustainability apprai
- Page 98 and 99: ensuring that environmental assessm
- Page 100 and 101: The second issue that raises some q
- Page 103 and 104: Chapter 7 A Comparative Description
- Page 105 and 106: system. This notion is reinforced b
- Page 107 and 108: Who decides?The authorities respons
- Page 109 and 110: plans at the municipal level (Impac
- Page 111 and 112: experience of assessing the plan’
- Page 113: preconditions for the introduction
- Page 117 and 118: the SEArequirements,i.e. whichplans
- Page 119 and 120: Chapter 8 FindingsThe aim of the re
- Page 121 and 122: importance of improved knowledge an
- Page 123 and 124: At the same time HB has had access
- Page 125 and 126: References and documentsAlfredsson,
- Page 127 and 128: Christoferson, I. (ed), (2001) Swed
- Page 129 and 130: Kørnøv, L. (1999) Integrating SEA
- Page 131 and 132: Sheate, W., Byron, H., Dagg, S. and
- Page 133 and 134: European Union’s publicationsEC (
- Page 135 and 136: English documents:Countryside Counc