SEA IN THE CONTEXT OF LANDTUSE PLANNING
SEA IN THE CONTEXT OF LANDTUSE PLANNING SEA IN THE CONTEXT OF LANDTUSE PLANNING
FIGURE 1.1. BASIC TYPES OF CASE-STUDY DESIGNS. BASED UPON YIN. (SOURCE:WWW.IDT.MDH.SE/PHD/COURSE/FALLSTUDIE).The research is based upon a multiple-case analysis, where the definition of a case as acountry, or more precisely, the institutional and administrative conditions that defines theplanning system. The case study approach applied in this research resembles multiple-casedesigns (figure 1.1). Certain aspects of the workings of each of the systems and their nationalcontexts are identified and compared between the cases.Empirical basisThe empirical material gathered for the research was based upon the principle of triangulationand include official documentation, including legislation and preparatory legal texts(förarbeten), regulations, guidance, evaluations and other official reports and records. Thetext in the national overviews in this thesis provides an overview of the material, legislation,regulations and guidance that has been issued before the 1st of January 2008. Materialavailable at a later stage is not included. Furthermore, interviews were conducted with keystakeholders at the national level in Iceland and Sweden. The interviews were open-ended andaimed at receiving supplementary insight into the implementation process. The author alsoparticipated 2002 – 2003 in a reference group appointed for the preparation of guidelines forthe implementation of the SEA directive in a Swedish legal context. The work was led by theSwedish Environmental Protection Agency and included representatives from the nationalauthorities and other key stakeholders, e.g. the Swedish Rail Association, the Swedish RoadAssociation, Swedish Association of Local Authorities and Regions, Stockholm CountyAdministrative Board etc.The research questions and the set of criteria considered to be relevant in different partsof the study were identified on the basis of extensive review of articles and written material14
on the subject, prior to the formal identification of the case studies as a part of the research.This included a review of SEA literature, including both research and practice reports, inorder to establish a basis of current discussions in SEA to date. Furthermore key publicationsin planning theory, as well as recently published articles debate current planning issues werereviewed as a part of the literature review, in order to identify relevance of issues discussed inrelation to SEA.Comparative analysisTwo major themes are in focus for the gathering of information from the case studies:• Firstly, aspects relating to the actual legal introduction of the contents of the directive2001/42/EC in the three countries; e.g. plans and programmes covered by the directive,the environmental assessment process (scoping, environmental reporting, consultation,relation to decision making, mitigation and follow-up).• Secondly, the aspects of land use planning in the countries studied, including the legalbasis, main actors, planning levels as well as other environmental initiatives.The information gathered by the case studies is analysed by a comparative analysis (Patton1990:402-406, 466-467). In the comparative analysis a set of indicators is chosen in order toidentify the pattern of convergences and differences (divergence) in the information gathered.The sampling of empirical information was carried out in two stages; firstly information wassampled in order to identify the research questions and secondly to identify the relevantaspect to be studied in the national case studies. The comparative description and analysis ofthe information gathered thus takes a starting point in the contextual aspects considered to beof relevance for the introduction of the directive; the national legal framework, the land-useplanning system, previous experience of applying SEA and the expectations attached to SEA.In the research the different modes of implementation are examined in the light ofsignificant characteristics of the planning system, such as; the administrative levels ofplanning, tiering of planning activities at different administrative levels, legal requirements onthe contents of the plans, government environmental policy and public participation. Theinteraction between SEA implementation modes and salient characteristics of the planningsystem is analysed and discussed on the basis on categories of implementation discussed byEmmelin and Lerman (2005):• Minimalist, i.e. with the objective of implementing the directive in the specific nationalcontext 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.In a study on the role of Strategic Environmental Assessment (SEA) in integrating theenvironment into strategic decision-making in all EU countries, as well as some non-EUcountries and international financial institutions, Sheate et al (2001) identified three keymodels of processes, institutions and communication mechanism utilised for environmentalintegration:• Constitutional/Legislative Model, i.e. specific legal provisions for environmentalprotection and integration in a country’s constitution or a ‘consolidated’ legislation orlegislation that imposes duties on public bodies.15
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on the subject, prior to the formal identification of the case studies as a part of the research.This included a review of <strong>SEA</strong> literature, including both research and practice reports, inorder to establish a basis of current discussions in <strong>SEA</strong> to date. Furthermore key publicationsin planning theory, as well as recently published articles debate current planning issues werereviewed as a part of the literature review, in order to identify relevance of issues discussed inrelation to <strong>SEA</strong>.Comparative analysisTwo major themes are in focus for the gathering of information from the case studies:• Firstly, aspects relating to the actual legal introduction of the contents of the directive2001/42/EC in the three countries; e.g. plans and programmes covered by the directive,the environmental assessment process (scoping, environmental reporting, consultation,relation to decision making, mitigation and follow-up).• Secondly, the aspects of land use planning in the countries studied, including the legalbasis, main actors, planning levels as well as other environmental initiatives.The information gathered by the case studies is analysed by a comparative analysis (Patton1990:402-406, 466-467). In the comparative analysis a set of indicators is chosen in order toidentify the pattern of convergences and differences (divergence) in the information gathered.The sampling of empirical information was carried out in two stages; firstly information wassampled in order to identify the research questions and secondly to identify the relevantaspect to be studied in the national case studies. The comparative description and analysis ofthe information gathered thus takes a starting point in the contextual aspects considered to beof relevance for the introduction of the directive; the national legal framework, the land-useplanning system, previous experience of applying <strong>SEA</strong> and the expectations attached to <strong>SEA</strong>.In the research the different modes of implementation are examined in the light ofsignificant characteristics of the planning system, such as; the administrative levels ofplanning, tiering of planning activities at different administrative levels, legal requirements onthe contents of the plans, government environmental policy and public participation. Theinteraction between <strong>SEA</strong> implementation modes and salient characteristics of the planningsystem is analysed and discussed on the basis on categories of implementation discussed byEmmelin and Lerman (2005):• Minimalist, i.e. with the objective of implementing the directive in the specific nationalcontext 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.In a study on the role of Strategic Environmental Assessment (<strong>SEA</strong>) in integrating theenvironment into strategic decision-making in all EU countries, as well as some non-EUcountries and international financial institutions, Sheate et al (2001) identified three keymodels of processes, institutions and communication mechanism utilised for environmentalintegration:• Constitutional/Legislative Model, i.e. specific legal provisions for environmentalprotection and integration in a country’s constitution or a ‘consolidated’ legislation orlegislation that imposes duties on public bodies.15