SEA IN THE CONTEXT OF LANDTUSE PLANNING
SEA IN THE CONTEXT OF LANDTUSE PLANNING SEA IN THE CONTEXT OF LANDTUSE PLANNING
subsidies and green certificates), as well as legal instruments, is promoted as an effective wayof working towards the goals of sustainable development. The strategy promotes a broadersustainable assessment as an important instrument for the purposes of impact assessment“…at the international, as well as the national, regional and local levels in Sweden” (Comm2001/02:172).4.7.2 Sustainable development at the municipal levelAt the municipal level, extensive work has been carried out within the frame of Local Agenda21 (LA 21). 70% of Swedish municipalities have adopted local action plans(Miljödepartementet, 2002) and Sweden is the European country with the most widespreadengagement in LA 21 (Eckerberg 2001). According to Eckerberg the engagement in LA 21can be explained by support at the national level through campaigns, information andfunding, but in 1997 national support was introduced for local initiatives in the field ofecological sustainable development. In 2000 half of the Swedish municipalities had decided tointegrate the work on LA 21 in municipal comprehensive planning (Schulman and Troedson2001) and a detailed study of 10 municipalities has shown that integration of LA 21 andmunicipal comprehensive planning has led to environmental aspects receiving a larger part ofthe planning process as well as integration of different sectors (Eckerberg and Brundin 2000).Environmental quality norms and objectivesWith the introduction of the Environmental Code in 1999, new demands were made oncoordination between the environmental and the planning legislation. The requirements ofchapter 3 and 4 of the Environmental Code relating to management of water and land shallbe applied in planning and the provisions in chapter 5 on environmental quality norms(miljökvalitetsnormer) shall also be considered in planning. These requirements are a part ofthe cabinet’s and the parliament’s goal to develop the role of physical planning andcomprehensive municipal planning in the work for sustainable development (Riksrevisionen2005). Parallel to the growing interest in SEA, national environmental quality objectives weredeveloped and resulted in the parliament adopting 15 environmental quality objectives in1999 (Regeringskansliet 2001). The objectives are formulated with regard to nature’s capacityto absorb environmental impacts and focused mainly on aspects such as human health,biological diversity, cultural environment and nature. The national environmental qualityobjectives have been adopted at the regional and local levels, with the presentation of regionaland local environmental quality objectives. According to SAMS (Boverket, Naturvårdsverket 2000)the national environmental quality objectives provide an important framework for theimplementation of SEA. The relation between and coexistence of sustainability,environmental quality objectives and SEA was illustrated in the pilot study on SEAimplementation in municipal comprehensive planning, conducted by Bjarnadóttir andÅkerskog in 2003 (see below).However, the national environmental quality objectives (and indicators developed tomeasure them) have been criticized for focusing largely on aspects of the physicalenvironment and, as highlighted by Hedlund (2000), the choice of indicators is not purely ascientific issue, but needs to be identified and understood by several different stakeholders.Furthermore, the question arises as to whether the basis given for future SEA work with theexistence of the environmental indicators will lead the focus away from the over-arching aimsof the SEA process and will be instead preoccupied with developing methods to fulfil theenvironmental quality objectives?60
A pilot study on impact assessment in comprehensive municipal plans in Sweden (Bjarnadóttir andÅkerskog 2003), illustrated that the goal of sustainability was well established in all of the plans studiedand included in the overall aims of the plans. Several of the plans saw the requirement of impactassessment as a part of the planning process in order to achieve the greater goal of sustainability, whilein others the focus on sustainable development meant a move away from environmental emphasis,arguing that environmental issues cannot be looked at in isolation, i.e. without their economic and socialcontext. The general impression from the municipal plans studied is that when the municipalityconsiders the three aspects of sustainability simultaneously, the results are often quite general; it wasunclear which indicators were used in the impact assessment and the environmental aspects weregiven a lower priority as a consequence.The inclusion of national environmental quality objectives and their relation to the impact assessmentwork was prominent in the municipal plans studied. All of the municipal plans mentioned theenvironmental objectives as a framework for working with environmental issues in the plan, the nationalenvironmental objectives goals, the regional ones or environmental objectives developed in themunicipality.FIGURE 4.3. REFERENCE TO SUSTAINABLE DEVELOPMENT AND ENVIRONMENTAL QUALITY OBJECTIVES IN IMPACTASSESSMENT OF MUNICIPAL COMPREHENSIVE PLANS4.8 Discussion - the introduction of SEA in relation to the national planningsystemThe legal requirements on environmental integration in municipal comprehensive planninghave existed in Sweden during the last 30 years, but despite substantial progress in addressingenvironmental issues at the municipal level, the environmental integration in municipalcomprehensive planning is still in many cases a daily struggle (Asplund and Hilding-Rydevik2001, Håkansson 2005, Nilsson, 2001). Prior to the implementation of the Directive’srequirements in the Environmental Code, two alternatives for the introduction of the SEAdirective into existing legislation were discussed (Prop.2003/04:116). The first alternativeincluded the inclusion of the requirements into the existing legislation and the continuation ofthe existing requirements for impact assessment, e.g. the Environmental Code, the Planningand Building Act and the Road and Energy Acts. The second alternative was to integrate EIAand SEA procedures in a separate act. The advantage of this option was considered toprovide for more clarity, in particular with regard to the public and their ability to relate to asingle process (Lerman 2003). According to the committee revising the PBA and presentingoptions proposal for the legal implementation of the directive, the first option was consideredmore feasible as it would simplify the application of the process; linking the new requirementsto the existing requirements on EIA, and making use of existing experience in the field.Emmelin and Lerman (2005) describe the Swedish implementation of the directive asminimalist, with regard to the lack of clear objectives in respect of SEA, as well as a notablelack of clarity on several points relating to the application of the terminology of the directive.Furthermore, the government stated explicitly in instructions to the committee that thedirective should be introduced to Swedish legislation with as little disruption as possible(SOU 2003). Furthermore, the authors argue that the implementation of the directive intoSwedish law is coloured by a professional struggle between the spatial planning professionand an emerging environmental profession.A questionnaire survey carried out by the National Board for Housing and Planning in2006 (Boverket 2008) addressed the application of the requirements of SEA in the municipalcomprehensive planning. Several of the County Administrative Boards reported that themunicipalities have still to find the forms for addressing the environmental assessment andthere exists a substantial uncertainty on how those shall be handled in the plans and the61
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A pilot study on impact assessment in comprehensive municipal plans in Sweden (Bjarnadóttir andÅkerskog 2003), illustrated that the goal of sustainability was well established in all of the plans studiedand included in the overall aims of the plans. Several of the plans saw the requirement of impactassessment as a part of the planning process in order to achieve the greater goal of sustainability, whilein others the focus on sustainable development meant a move away from environmental emphasis,arguing that environmental issues cannot be looked at in isolation, i.e. without their economic and socialcontext. The general impression from the municipal plans studied is that when the municipalityconsiders the three aspects of sustainability simultaneously, the results are often quite general; it wasunclear which indicators were used in the impact assessment and the environmental aspects weregiven a lower priority as a consequence.The inclusion of national environmental quality objectives and their relation to the impact assessmentwork was prominent in the municipal plans studied. All of the municipal plans mentioned theenvironmental objectives as a framework for working with environmental issues in the plan, the nationalenvironmental objectives goals, the regional ones or environmental objectives developed in themunicipality.FIGURE 4.3. REFERENCE TO SUSTA<strong>IN</strong>ABLE DEVELOPMENT AND ENVIRONMENTAL QUALITY OBJECTIVES <strong>IN</strong> IMPACTASSESSMENT <strong>OF</strong> MUNICIPAL COMPREHENSIVE PLANS4.8 Discussion - the introduction of <strong>SEA</strong> in relation to the national planningsystemThe legal requirements on environmental integration in municipal comprehensive planninghave existed in Sweden during the last 30 years, but despite substantial progress in addressingenvironmental issues at the municipal level, the environmental integration in municipalcomprehensive planning is still in many cases a daily struggle (Asplund and Hilding-Rydevik2001, Håkansson 2005, Nilsson, 2001). Prior to the implementation of the Directive’srequirements in the Environmental Code, two alternatives for the introduction of the <strong>SEA</strong>directive into existing legislation were discussed (Prop.2003/04:116). The first alternativeincluded the inclusion of the requirements into the existing legislation and the continuation ofthe existing requirements for impact assessment, e.g. the Environmental Code, the Planningand Building Act and the Road and Energy Acts. The second alternative was to integrate EIAand <strong>SEA</strong> procedures in a separate act. The advantage of this option was considered toprovide for more clarity, in particular with regard to the public and their ability to relate to asingle process (Lerman 2003). According to the committee revising the PBA and presentingoptions proposal for the legal implementation of the directive, the first option was consideredmore feasible as it would simplify the application of the process; linking the new requirementsto the existing requirements on EIA, and making use of existing experience in the field.Emmelin and Lerman (2005) describe the Swedish implementation of the directive asminimalist, with regard to the lack of clear objectives in respect of <strong>SEA</strong>, as well as a notablelack of clarity on several points relating to the application of the terminology of the directive.Furthermore, the government stated explicitly in instructions to the committee that thedirective should be introduced to Swedish legislation with as little disruption as possible(SOU 2003). Furthermore, the authors argue that the implementation of the directive intoSwedish law is coloured by a professional struggle between the spatial planning professionand an emerging environmental profession.A questionnaire survey carried out by the National Board for Housing and Planning in2006 (Boverket 2008) addressed the application of the requirements of <strong>SEA</strong> in the municipalcomprehensive planning. Several of the County Administrative Boards reported that themunicipalities have still to find the forms for addressing the environmental assessment andthere exists a substantial uncertainty on how those shall be handled in the plans and the61