With regard to the effects of the directive at the local levels, all the countries have hadsome experience of developing a tool to systematically assess the effects of strategic plans atthe municipal levels; Impact Assessment Sweden, Environmental Assessment in Iceland andSustainability Appraisal in England. From the review of the legal introduction of the <strong>SEA</strong>directive to the three countries’ national planning systems, it is obvious that the systems areall undergoing periods of fundamental change. In each of the countries studied, the planninglegislation has either recently been revised or is currently under revision. The introduction ofthe <strong>SEA</strong> directive generally then coincides with those processes. In the planning theoryliterature a shift in emphasise in planning practice is identified, i.e. a move from rationalistdecision making to a communicative approach to planning. At the same time, new modes ofplanning are surfacing in the form of strategies, visions, partnerships, and other non-bindingmeasures as the guiding principles for municipal development. The changes facing statutoryland use planning are thus not only emerging through institutional measures, but also throughchanges in current practice. These changes correlate to the discussion in the planningliterature that highlights a shift form an administrative regulatory practice to non-statutory or‘negotiative’ initiatives, (Cars 1992) or as put by Healey (1997): “In many of Europe’s planningsystems, the formal machinery for articulating strategies has become discredited and formal systems have ceasedto be the key arenas and procedures for spatial strategy-making. This new impulse towards strategic planninghas however been taking place rather informally, beyond the formal arenas provided by the planning systemitself”. According to Emmelin and Lerman (2005) there has even emerged resistance to theformalised nature of planning, where the formal participatory elements in planning could beseen as a hindrance to strategic decision-making. This view is furthermore matched by arecent survey carried out by The National Board of Housing, Building and Planning toSwedish municipal planning authorities in 2006.8.3 Relevance for future applicationWith regard to the relationship between the existing context, the actual impacts of thedirective and the notion of ‘effectiveness’, the introduction of the <strong>SEA</strong> requirements intonational institutional framework is too recent for it to be possible to draw conclusions on theeffects of the implementation. Drawing conclusions on the actual contents of the legislationsthat make statutory interpretation of the <strong>SEA</strong> demands, the formal aims of <strong>SEA</strong>, illustrated inthe national legislation discussed in the licentiate thesis, do however reflect to a large degreethe aims of the <strong>SEA</strong> directive, with an emphasis on both environmental objectives and thepromotion of sustainable development. However, these objectives are sufficiently imprecisesuch that they could be interpreted in different ways in the different systems. Moreover,within the context of the national overviews it became clear that the introduction andimplementation of the directive would play a different role in the current reforms of thenational planning systems.Finally, it can be stated that the effects of the introduction of the <strong>SEA</strong> directive onexisting planning practice relate essentially to the underlying expectations in respect of thedirective, its relation to the existing context and the willingness to commit to its intentions. Ineffect; whether <strong>SEA</strong> shall be adapted to the prevailing planning practice by illustrating theenvironmental impacts of the proposals already decided, or whether the introduction of <strong>SEA</strong>is expected to contribute to a change in the existing planning practice.8.4 Challenges encountered in the researchThe information assembled from the different countries was not always comparable. This hasresulted in varying level of detail as well as different emphasis in the national chapters. For anexample limited academic research and evaluation results were available in the field of townplanning and environmental assessment regarding Iceland compared to the other countries.116
At the same time HB has had access to officials and experts at the national level how havebeen involved and have had first-hand knowledge of the process of introducing the Directive2001/42/EC to the Icelandic system. In Sweden HB has had both access to officials, partlyparticipated in the process as well as a large amount of research results in the field. In the caseof England HB has not carried out complementary interviews, but has relied on writtendocumentation, as well as HB got an glimpse of the current academic planning discussionduring a brief stay as a visiting PhD student at the Planning Department at the University ofSheffield in the autumn of 2005.8.5 Issues for further studiesHaving shown the importance of the national context in understanding the possibleoutcomes of the directive, empirical evidence from the actual application of the directive inplanning would be a valuable continuation of the research. An interesting aspect in thisrespect would be study the application of <strong>SEA</strong> to the planning process at the municipalplanning level, which is the most compatible between the countries; hence the three countrieshave a legal requirement of preparing spatial plans at the municipal level, which fall under thedirective’s requirements in all the three countries. Such as study could have a special focus onthe aspects identified as important at the national planning level, the variation in the legalcontext of the <strong>SEA</strong> introduction, the level of and the type of guidance provided nationallyand the expectations towards the directive. Such as study would provide not only insights onthe potential effect of the <strong>SEA</strong> directive in the different planning contexts, but also the statusand development of the municipal planning system and the integration of environmentalconsiderations in the system with respect to practice prior to and after the <strong>SEA</strong> introduction.117
- 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 and 114: preconditions for the introduction
- Page 115 and 116: that the directive has spurred the
- Page 117 and 118: the SEArequirements,i.e. whichplans
- Page 119 and 120: Chapter 8 FindingsThe aim of the re
- Page 121: importance of improved knowledge an
- 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