Strategic Environmental Assessment – necessity, principles and specificities Monika Sabeva, University of National and World Economy, Sofia, Bulgaria e-mail:

Slides:



Advertisements
Similar presentations
THE GHANA POVERTY REDUCTION STRATEGY Integration and Progress of Environmental Issues By Winfred Nelson NDPC November
Advertisements

SEA & ETC Strategic Environmental Assessment and European Territorial Cooperation programmes Annual meeting with the Managing Authorities of the ETC programmes.
ENEA, 12. September 2005 WWF Handbook and Score-card Presentation by Stefanie Lang,
Community Strategic Guidelines DG AGRI, July 2005 Rural Development.
Health impact assessment explained
INTERNATIONAL UNION FOR CONSERVATION OF NATURE. 2 Implemented in 12 countries of Africa, Asia, Latin America and the Middle East, through IUCN regional.
1 Strategic Environmental Assessment and SFs Operational Programmes: An assessment Jonathan Parker DG ENV ENVIRONMENT EUROPEAN COMMISSION Aarhus Workshop.
Marine Strategy Framework Directive: Goals and Challenges
1 CEER How to balance the public’s concerns and critical infrastructure construction Matti Vainio, Deputy HoU DG ENV – C.5, European Commission.
Lecture(2) Instructor : Dr. Abed Al-Majed Nassar
AN INTRODUCTION TO STRATEGIC ENVIRONMENTAL ASSESSMENT
Moving towards a more comprehensive planning SEA and indicators Per Christensen Aalborg University Denmark.
ENVIRONMENTAL MANAGEMENT PLAN
Secretariat to the Espoo Convention and its Protocol on SEA
 Sustainable development : one of the most important features of modern society, meeting our needs without threatening the needs of future generations.
The Knowledge Resources Guide The SUVOT Project Sustainable and Vocational Tourism Rimini, 20 October 2005.
SEEA Experimental Ecosystem Accounts: A Proposed Outline and Road Map Sixth Meeting of the UN Committee of Experts on Environmental-Economic Accounting.
The Marine Strategy Framework Directive 17th March 2010, Newcastle North Sea Stakeholders Conference Leo de Vrees European Commission (DG Environment,
Peter Defranceschi ICLEI - Local Governments for Sustainability An Introduction European Commission GPP Training Toolkit.
Strategic Environmental Assessment and environmental issues in programme evaluation Ivana Capozza Italian Evaluation Units Open Days Roma, July 5, 2006.
The model Modelling best practice in SEA a 10-step presentation.
Environmental Impact Assessment (EIA): Overview
EATIA (‘ESPON and Territorial Impact Assessment’): Developing a bottom-up approach for the territorial impact assessment (TIA) of EU policy proposals at.
3 September UNDERSTANDING THE SEA 20 th May 2013 Presented by: K. Florence.
Engaging with stakeholders: Adding value to the energy system 32nd Annual Conference of the International Association for Impact Assessment Porto Pedro.
The Aarhus & Espoo Conventions Making implementation work for stakeholders.
Guidance for AONB Partnership Members Welsh Member Training January 26/
Environment integration in EC development co-operation Approaches for the programming phase Jean-Paul Ledant (HDE) Help Desk Environment
Croatian Report on new Environmental Protection Law Josipa Blažević-Perušić, B.Sc. Arch. State Secretary Anita Pokrovac-Patekar, B.Sc. Pharm. Senior Environmental.
Contribution of the Territorial Cooperation Programmes to the EU Strategy for the Danube Region Kiril Geratliev, Director General “Territorial Cooperation.
Project design & Planning The Logical Framework Approach An Over View Icelandic International Development Agency (ICEIDA) Iceland United Nations University.
Wetlands and Poverty Reduction Project Anglophone regional practitioners training course MODULE 3 POLICY SETTING AND ADVOCACY By Teddy Tindamanyire, Isah.
TOPIC 12 STAKEHOLDERS AND SUSTAINABILITY. Introduction to Agenda 21 The Earth Summit held in Rio De Janerio, Brazil was attended by 178 country leaders.
Strategic Priorities of the NWE INTERREG IVB Programme Harry Knottley, UK representative in the International Working Party Lille, 5th March 2007.
Environmental Management System Definitions
Case study: SEA for land-use plan amendments of Krasna Hora municipality.
Integrated Risk Management Charles Yoe, PhD Institute for Water Resources 2009.
STRATEGIC ENVIRONMENTAL ASSESSMENT METHODOLOGY AND TECHNIQUES.
Recommendation 2001/331/EC: Review and relation to sectoral inspection requirements Miroslav Angelov European Commission DG Environment, Unit A 1 Enforcement,
PP 4.1: IWRM Planning Framework. 2 Module Objective and Scope Participants acquire knowledge of the Principles of Good Basin Planning and can apply the.
Approach to GEF IW SCS Impact Evaluation Aaron Zazueta Reference Group Meeting Bangkok, Thailand September 27, 2010.
Training Resource Manual on Integrated Assessment Session UNEP-UNCTAD CBTF Process of an Integrated Assessment Session 2.
Environmental Impact Assessment in the Slovak republic.
Implementation and follow up Critically important but relatively neglected stages of EIA process Surveillance, monitoring, auditing, evaluation and other.
PPSD in specific sectors in Bulgaria - Regional Plans for Development National Programme for Ports Development (2006 – 2015) Vania Grigorova, Jacquelina.
SEA in the Czech Republic Prague, 24 September 2008.
Implementation of critical studies necessary to promote better planning and efficient management of hydropower projects in an Int’l River Basin context.
Environment and Disaster Planning Hari Srinivas, GDRC Rajib Shaw, Kyoto University Contents of the presentation: -What is the problem? -Precautionary Principles.
Kathy Corbiere Service Delivery and Performance Commission
River Basin Management Planning Cath Preston Senior Planning Officer (River Basin Planning) 2 nd March 2006.
DEVELOPING THE WORK PLAN
URBAN STREAM REHABILITATION. The URBEM Framework.
UNEP EIA Training Resource ManualTopic 14Slide 1 What is SEA? F systematic, transparent process F instrument for decision-making F addresses environmental.
Adaptation Discourses and Modes of Governance in Swiss Alpine Regions Alexander Widmer & Christian Hirschi Symposium “The Governance of Adaptation”, Amsterdam,
Pilot Project on implementation of SEA for regional planning in Ukraine Prof. Dr. Michael Schmidt Dmitry Palekhov Brandenburg University of Technology.
DG ENV Environmental assessment procedures for energy infrastructure projects of common interest (PCIs)
FACULTY OF LAW, UNIVERSITY OF OSLO The principle of integration and its dilemmas Hans Chr. Bugge Professor of Environmental Law University of Oslo.
State Regulation in the Natural Monopoly Sphere Agency of the Republic of Kazakhstan on Regulation of Natural Monopolies ALMATY – 2006.
EIAScreening6(Gajaseni, 2007)1 II. Scoping. EIAScreening6(Gajaseni, 2007)2 Scoping Definition: is a process of interaction between the interested public,
TAIEX-REGIO Workshop on Applying the Partnership Principle in the European Structural and Investment Funds Bratislava, 20/05/2016 Involvement of Partners.
Strategic Environmental Assessment for the Operative Programmes Anita Gulam Ana Kovačević Ministry of Environmental and Nature Protection, Republic of.
Business environment in the EU Prepared by Dr. Endre Domonkos (PhD)
ENVIRONMENTAL ASSESSMENT TOOLS
The role of the Passport Indicators in Monitoring PFM Strategy
Communication and Consultation with Interested Parties by the RB
Nick Bonvoisin Secretary to the Convention on the
Progress of the preparations for a White Paper on Adaptation to Climate Change Water Directors’ meeting Slovenia June 2008 Marieke van Nood, Unit.
Strategic Environmental Assessment (SEA)
When and how to best consider the provision of the Habitats directive
INNOVATION DEALS: A NEW APPROACH TO REGULATION
Presentation transcript:

Strategic Environmental Assessment – necessity, principles and specificities Monika Sabeva, University of National and World Economy, Sofia, Bulgaria

Introduction With the development of market economy, modernization of manufacturing activities and the globalization of all spheres of public life, it now becomes clear that the pace of economic growth may decrease and even to acquire a negative entry, under the influence of environmental pollution, natural resource depletion, reducing bioproductivity of land and continuously growing population. This requires an assessment of environmental risks, their management, reduction and/or prevention. For this purpose a number of methods and approaches for environmental assessment are established. 2

Introduction Environmental assessment is an important tool for integrating environmental considerations in preparation and adoption of certain plans and programs which are likely to have significant effects on the environment. Strategic Environmental Assessment is carried out for politics, plans and programs. It constitutes a systematic evaluation process of the environmental consequences of application of relevant politics, plans and programs. 3

The purpose of SEA The purpose of SEA is to render an account of environmental issues at the earliest stage of development of strategic planning decisions, when determining the territorial scope and evaluating the possible impacts of investment proposals in global strategies and development plans, and to make this process more transparent through consultation and participation. This assessment provides decision makers the required information to enable the consideration of the potential environmental hazards from the implementation of the plan/program. 4

Objects and subjects of SEA Objects of SEA are strategies, plans and programs in industry, energy, agriculture, forestry, tourism, transport, mining of underground and ground resources, water use and management of water resources, fisheries, spatial planning and land use, waste management, electronic messages, when these plans and programs outline the framework for future development of investment proposals. Subjects of SEA are the Minister of Environment and Waters, and the Directors of Regional Inspectorate of Environment and Waters (RIEW). These government bodies are authorized to give opinions in validation the national and regional plans and programs. 5

Basic SEA principles Principle of integration; Principle of dialogue; Principle of responsibility for reduction or complete elimination of the environmental impacts ; Willingness to defend decisions taken and to eliminate adverse effects on environment; Principle of awareness; Principle of flexibility; Principle of democracy. 6

Stages of SEA SEA, under the SEA Directive, includes the following steps: Screening; Scoping; Documenting the environmental conditions; Determining the possible (non-marginal) environmental impacts; Informing and consulting the public; Impact of the decision; Monitoring. 7

Evaluation of alternatives The different alternatives, developed in the planning process are evaluated and then one of them is selected and is developed in details. It is necessary to determine whether the alternatives meet the environmental objectives. During this assessment the following methods are used: Determining the qualities of the impact by an impact matrix; Preparation of questionnaires, interviews and discussions, appropriate for gathering information – through this method it is easier to reach consensus and transparency; Checklists; Trend analysis; Geographic Information Systems; Analysis of Ecosystems and Biodiversity; Application of diagrams, networks, systems and other means of explaining and illustrating the cause-effect relations and determining both direct and cumulative impacts; Expert assessment. 8

Contents of the SEA report As any other procedure, SEA ends up with a detailed report that contains: Description of main objectives of the plan/program and relations with other plans/programs; In-depth analysis and evaluation of all environmental issues relevant to the procedure; Assessment of environmental impacts of the chosen; Describing the results of the environmental assessment (justification and summary of the decision-makers); Determining the environmental objectives of the plan/program of the relevant sector (area); Evaluation of different alternatives of the plan/program; Measures for monitoring and reducing the impacts of the selected alternative of the plan/program. 9

Characteristics of the procedure SEA procedure is distinguished by the following features: Public participation should be an integral part of the environmental assessment of plans/programs. The form of participation should be consistent with the nature and scope of the problems and to reflect the interests and values of the affected parties; Integration of the planning process with the process of environmental assessment and continuous contact between the two teams – The planning and environmental assessment teams should work in parallel and organize joint discussion of the results at every stage of planning; Successful consultations among stakeholders – they can be held in different ways. 10

Necessity of SEA The assessment system is needed due to the following basic positive and negative characteristics of the method: Integration of SEA can not be achieved by adjusting the existing EIA for a project to the relevant legislation, procedures and forms. SEA has new methodological and procedural requirements. Particular efforts are needed for identifying the indirect, the secondary and the cumulative impacts With increasing the awareness of the issues related to environment and sustainable development on a political level and in parallel with the development of environmental management systems (EMS) in government and industry, issues related to environmental protection become more important in the process of decision making SEA can be applied to a wide range of strategic actions at all levels (international, national, regional, local), sectors and resources, plans and politics and in terms on fundamentally different issues. 11

Political and institutional context It defines the objective of strategic actions and determines what can or can not be done in strategic plan. This step involves identifying of: The strategic actions, which are to be prepared and a response to the questions why these exact actions will be prepared; Other strategies that support or limit the forthcoming strategic actions; Current opportunities and practices for protecting the environment; Contemporary approaches to social issues; Other institutional factors such as: who has the most important role in taking the key decisions in the field; what determines the funding; is cooperation with other organizations that are not local a common practice, etc. 12

Technical and procedural limitations of SEA Relative lack of case studies and experience of SEA Decision-makers, competent authorities and stakeholders must be aware that SEA is inherently a political process, and should ensure that SEA informs decisions but does not make them; Each SEA system and methodology should be able to cope with many issues – a more nebulous decision-making process, uncertainty, larger scales and induced, secondary and cumulative impacts. The techniques used in SEA are often a combination of those used in traditional policy analysis or in EIA; SEA might be seen as a political act aiming to mislead voters that politicians care about the environment, because many problems are not completely developed, but the focus is on some of their individual aspects, which leads to partial solutions. 13

Basic information needed before initiating SEA What is the level (policy, plan, program) and scale (international, national, national, regional, local) of the strategic action? What is the time period of the strategic action? Is the strategic action one-off or cyclical? Is the strategic action for a sector (e.g. waste, energy); or a land use plan for an area (e.g. region, local authority); or something different still? Who is the competent authority, and what other stakeholders are involved in developing the strategic action? Is the competent authority a public or a private agency? 14

Development of objectives and indicators of SEA It is good practice for SEA objectives to focus on outcomes (or ends), not how the outcomes will be achieved ("inputs" or means). SEA objectives can be supported by a list of more detailed criteria or questions. The development of SEA objectives and indicators and the collection of baseline information should inform each other. As the SEA objectives become clearer, they should help to focus (or restrict) the collection of baseline information, whilst the baseline information should help to identify which SEA objectives are of most concern for the project. Each SEA objective should be genuinely needed and should not duplicate or overlap with other objectives. Experience suggests that 8 to 16 objectives are normally enough to cover the range of topics needed for SEA and to keep the process efficient and manageable. SEA objectives should be linked to indicators which measure progress or otherwise towards or away from them. 15

SEA indicators Indicators are directed to improving the monitoring and implementation of the Rural Development Program and are divided into five groups: Basic indicators related to objectives; Basic indicators related to context; Output indicators; Result indicators; Impact indicators. They could be horizontal or could be distributed in the respective axes: Axis 1 Improving the competitiveness of the agricultural and forestry sector; Axis 2, Improving the environment and the countryside through land management; Axis 3 Improving the quality of life in rural areas and encouraging diversification of economic activity and Axis Leader+ 16

Conclusions The relationship between mankind and environment is a prerequisite for occurrence of a number of amendments in it, which can significantly deteriorate its condition. This threatens ecosystems, social stability, health condition and economic development and requires the need of strict measures towards conservation and prevention (or limiting) the adverse impacts. The environmental assessment of all strategic and planning documents on different levels becomes a major tool for maintaining the ecological stability. SEA is one of the basic tools for preventive control and is also an integral part of the process of development and adoption of plans, programs and politics. Its main objective is achieving a sustainable development, minimizing the adverse impacts on environment and improving its quality. SEA should ensure that plans and programs take into account the potential environmental impacts they cause. Strategic Environmental Assessment refers to the policy of the EU and in most cases takes place before Environmental Impact Assessment. 17

THANK YOU FOR THE ATTENTION 18