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Updated to: 16 February 2015Download as PDF
Country contact on SEA
Contact details for the country contact on SEA.
Country's planning system
Brief description of planning practice, specifically whether it take place more often at centralised or decentralised level, what kind of national level planning and sectoral planning takes place, etc.
In Rwanda, the Ministry of Finance and Economic Planning (MINECOFIN) is responsible for planning issues, particularly its Directorate "National Development Planning & Research". The Directorate's function is among others to ensure that the planning function in both, central and local governments, is aligned to national priorities. In general, policies, plans and programs are developed by sector ministries and implemented by the respective line institutions.
History of SEA
Brief description of the history of SEA in the country, including when it was introduced and any major milestones in its development.
The national strategy 'Vision 2020' already included the need for protection of the environment through sustainable resource management. The need for improved capacities for environment and resource managment was further recognized during the formulation of the first Poverty Reduction Strategy Paper (PRSP 1, 2002-2005). The Constitution of the Republic of Rwanda, adopted in June 2003, ensures the protection and sustainable management of environment and encourages rational use of natural resources. With the Organic Law (No. 04/2005) SEA (such as EIA) was introduced into legislation. It requires that programmes, plans and policies that may affect the environment shall be subjected to environmental impact assessment before obtaining authorisation for implementation. It thus implies that environmental assessment would have a broader scope than the project-based EIA and provides the legal provision for an SEA instrument. However, it does not specify what form of environmental assessment would be required. In 2005, the Government of Rwanda joined the UNDP/UNEP Poverty Environment Initiative (PEI) to develop a strategy to mainstream environment into
national planning processes and economic development strategies. In 2009, REMA started the implementation of the Decentralized Environment Management Project (DEMP). The PEI and DEMP promoted SEA further and the Economic Development and Poverty Reduction Strategy (EDPRS) identified the need for the development of specific SEA guidelines. Such SEA guidelines were issued in 2011 by REMA.
Legal framework for SEA
Name of first enabling legislation that sets the framework for SEA.
Organic Law (No.04/2005)
Approving authority of enabling law
The authority that approved the enabling law for SEA.
The president has approved the Organic Law.
First national detailed SEA regulation
First national detailed regulation (procedural requirements) for SEA, through which SEA was operationalized.
A ministerial order that further defines the procedural requirements for the SEA process in Rwanda is under development.
Any government issued guidelines on SEA (general or sectoral) are listed here, as well as the authority that issued each. Describes the legal status of the guidelines.
Guidelines and procedures for SEA were published in June 2011 by REMA in collaboration with One-UN Rwanda to complement the existing EIA guidelines for Rwanda.These guidelines do not contain clear procedural arrangements on roles and responsibilities for SEA though.
The objective of SEA as stated in the above described legal basis.
The SEA guidelines (2011) mention SEA to enable the assessment of potential effects of policy, plans and programs on the environment through processes involving broad stakeholder participation. They further mention that SEA aims to enhance environmental awareness, to integrate environmental sustainability into decision making, to facilitate coordinated action across development sectors and to contribute to the attainment of environmentally sound, integrated, and balanced development policies, planning, and programs. It further mentions that SEA supports Rwanda's committment to several international agreements.
Scope of SEA application
Describes for which planning processes (at policy, programme and plan level) SEA is required.
In the EIA guidelines (2006) it is mentioned that SEA is the assessment of impacts of policies, plans, programmes (PPP) which are higher than the project level. The guidelines for SEA maintain this scope of SEA.
Exemptions from SEA application
Are any specific types of plans explicitly excluded from SEA application?
No list of PPPs that are exempted from SEA has been developed yet when the SEA guidelines were issued in 2011, but it is expected that such a list will be gazetted in a Ministerial Order on the recommendation of REMA as the regulatory agency.
Describes the current overall SEA approach. Specifically: Has the country's SEA procedure been modeled on the existing EIA approach? Or has a separate SEA approach been developed?
The SEA guidelines aim to expand the application of environmental assessment principles and practices to the formulation and implementation of policies, plans and programs. The SEA guidelines also incorporate concepts and practices of Environmental Security Assessment (ESA), which are designed to inform strategic decision-making that integrates environmental protection, economic growth, and social well-being.
SEA tiering with EIA
Are there any provisions for tiering of EIA and SEA?
The guidelines for EIA stress the importance of tiering of EIA and SEA. They mention that SEA and project level EIA have a close tiering relationship, similar to tiering from policy to project.
The SEA guidelines specify that SEA complements and strengthens EIA at the project level by: identifying prior information needs and potential impacts; addressing strategic issues and concerns that may relate to project justification; and streamlining the project review process.
Institutional setting for SEA
Central SEA authority
Is there a central authority in charge of the SEA system as a whole, responsible for issuing guidelines etc? If so, is it independent or linked to a higher body (e.g. ministry)?
Such as for EIA, the Rwanda Environmental Management Authority (REMA) is the central authority responsible for SEA. REMA is required by law to oversee environmental assessment requirements in policies, plans and programs and advice the Government on policies, strategies, and legislation related to the managment of the environment. Under this mandate, REMA develops facilitative and legal instruments, such as SEA guidelines.
The REMA operates under the Ministry of Natural resources (MINIRENA), which supervises the REMA. It is governed by a board of directors comprising of 7 people that are appointed by the Prime Minister on advice from the Minister responsible for the environment.
Mandate for exemption of SEA obligation
Is there a legal mandate for a competent authority to make exemptions of SEA obligation? If yes, under which conditions (e.g. national security, disasters or no conditions/when deemed necessary)?
The ministerial order on exemptions of SEA obligation is not yet available.
(De)centralisation of SEA mandates
Are SEA mandates (de)centralised? Vertical decentralization refers to the extent to which the responsibility for SEA processes is delegated by the central government to the provincial or local authorities. Sectoral or horizontal decentralization refers to the reassignment of decision-making authority on SEA to government units on a sectoral basis.
SEA mandates are centralized at REMA
Initiator of the SEA
Who initiates the SEA? Should the plan owner initiate and undertake the SEA or is an environmental authority responsible for undertaking the SEA. If an authority is responsible, which authority and at which level?
According to the SEA guidelines, the lead agency, which formulates and implements a policy, plan or programme, is responsible for conducting an SEA for the policy, plan or program. It is, however, common practice for a team of independent experts to be appointed to conduct the SEA on behalf of a PPP formulation team.
Overview SEA procedure
Short text characterizing the overall SEA procedure. If relevant, interesting aspects of the SEA procedure are mentioned such as: which procedural steps are part of the SEA procedure and are they based on procedures defined for EIA (screening, scoping ect)? How are they related to each other? Does the legal text provide specifications regarding the timing of the start of the SEA procedure within t
The SEA guidelines describe the SEA process and procedures. The conceptual basis for these guidelines follows an approach developed by the United Nations Commission for Europe. It follows 10 steps:
- Identifying the main characteristics of the policy, plan or program (PPP)
- Analyzing the PPP formulation process
- Determining the need for SEA for a PPP
- Determining the nature and extent of impacts
- Determining content and level of detail in SEA report
- Consultation with relevant authorities
- Public consultation
- Ensuring SEA integration in the PPP process
- Coordinating SEA within the PPP process
- Monitoring SEA within the PPP process.
Screening requirement and authority
Is a formal screening decision required? And if so, which authority is responsible for this decision? Is the decision published?
As the description of the screening process indicates, the legally non-binding SEA Guidelines ask for a final screening decision for some of the PPPs only. This decision is taken by REMA.
Describes the screening process for SEA (if any), who is involved and who is responsible. What kind documentation on the SEA needs to be submitted for screening?
The screening process includes three main steps. The SEA guidelines suggest that as a first step of the SEA procedure the main characteristics of the targeted PPP are identified. This information will help to determine whether or not there is a need to conduct an SEA for the particular PPP and if there is a need to establish the context for the SEA objectives, outcomes, and report recommendations. The guidelines provide a list of questions to determine the characteristics of the PPP. Thereafter, the PPP formulation process is analysed to find out whether or not the environmental assessment requirements have been or will be met, if consultations with relevant government authorities and the public have taken place and what the timing of these activities was. The general SEA guidelines provide questions to guide this analysis as well as a framework for the analysis in their Appendix 2.
With the collected information it is then decided whether or not an SEA is required for the respective PPP. Up to the moment of the issuing of the SEA guidelines, no list of PPPs subject to and those exempt from SEA has yet been gazetted. Such a list
was then expected to be published soon though. The SEA guidelines nevertheless already indicate how the process leading to the screening decision for PPP will be built up. Firstly, it is assessed whether the PPP is exempted from SEA (list has yet to be established). Then it is determined if the PPP is likely to cause negative environmental effects. The SEA guidelines provide criteria to establish the likelihood of a PPP causing significant environmental effects on a case-by-case basis (includes criteria based on characteristics of PPP and of the effects and of the area likely to be affected). If it is likely to do so, it is checked if the PPP relates to a small area at a local level or involves a minor modification to a PPP. If this is not the case, an SEA is directly required. If this is the case, the PPP is subject to a final screening decision carried out by REMA. In case the PPP does not belong to a high impact sector, the opinion of the REMA is sought in an additional process referred to as pre-screening. REMA can exempt this PPP or recommend that a final screening has to take place.
Maximum number of (working) days between submission of the screening request and the screening decision.
Identification of stakeholders
Are stakeholders identified early on in the SEA? Who is responsible for identifying the stakeholders? Is a communication plan developed (addressing public and government engagement, disclosure, etc?).
The key stakeholders are identified as part of the scoping process.
Setting SEA objectives
Is there an early discussion on the objectives for the SEA (i.e. How it will support planning, how it will be integrated into the planning process)? Which stakeholders are involved? Are the outcomes of this discussion documented?
Implementing the SEA
Is there a distinct scoping process? Who is responsible? Who is involved? What methods (if any) are prescribed (overlays, matrices, etc)?
The SEA guidelines suggest that after it was determined that a PPP is subject to an SEA, the nature and extent of environmental impacts to be measured must be identified and a study approach designed. The scoping exercise involves the identification of key stakeholders as well as the establishment of data requirements, the level of detail of the study and the study program. The SEA guidelines provide a list of questions that may guide the scoping process and analytic categories that may be used for scoping issues in Appendix 3. A team of professional experts finally formulates the scope of work as Terms of Reference for SEA. International experts can be asked to give advice on the scope of the SEA as it was the case for the IWRM support programme where the NCEA was involved.
Participation in scoping
If here is distinct scoping, is participation part of this process? Who is involved and how?
The SEA guidelines specify that the scoping process involves the identification of key stakeholders and that for the formulation of the Terms of Reference for SEA, input from the participation of the public shall be considered.
Outcome of scoping
What are the expected outcomes of the scoping? e.g. decision criteria and suitable indicators of desired outcomes identified? If a ToR/scoping document is produced, what are the content requirements if any? Is the ToR reviewed? Is the outcome widely available?
The SEA guidelines mention that Terms of References may be formulated to define the scope of work, but no further specifications regarding its content, public availability or a possible review process is given.
Are there any specific requirements for data collection (for example, on protected areas)?
Are there any requirements for the alternatives to be considered in the SEA? How should alternatives be selected, ranked, compared?
The SEA guidelines determine that alternative options for the PPP should be considered before embarking on analyzing the nature and extent of impacts of the proposed PPP. For this, a well-documented "do nothing"option is used as the point of reference. Potential positive and negative impacts (direct, indirect, cumulative and/or large-scale impacts) of alternative options then need to be identified. A format for presenting alternative options within the PPP and their impacts is provided in Appendix 4.
Assessment/mitigation of effects
What are the specific requirements for assessment and mitigation of impacts as part of SEA? Any specific methods prescribed?
The SEA guidelines mention the following impact assessment methods: Scenario development, risk assessment, policy impact matrix, predictive and simulation models, significance thresholds, GIS capacity/habitat analysis, cost/benefit analysis, least cost analysis, multi-criteria analysis.
The most suitable method is chosen according to professional experience and judgement of the SEA team members.
Is the institutional setting for implementation of the plan analysed? Is there explicit attention for the identification of opportunities to strengthen environmental constituencies?
The SEA guidelines mention that recommendations for institutional strengthening should be part of the SEA report, thus it can be assumed that such an analysis takes place.
Are the assessment results documented?
An SEA report is formulated.
Content of SEA report
If documentation is required, what should be contained in the SEA report?
The SEA guidelines list the content of the SEA report: It should contain information on the content and the main objectives of the strategic decision drafted. Also environmental protection and social objectives that are established at international, national, regional and local levels which are relevant to the SEA report, shall be assessed and discussed. Further the current state of the environmental and social aspects and the likely evolution of this state is to be mentioned. Then the environment and social conditions likely to be affected have to be identified (Appendix 1 of the SEA guidelines provides a list of questions that help to capture the qualitative dimensions of these environmental and social issues). Further the likely significant impacts on the environment and socio-economic aspects have to be presented (including cumulative, indirect and transboundary impacts). Reactions, suggestions and objections from stakeholders have to be included as well as the eligibility for carbon credits. An overview of the data requirements, quality and data gaps has to be given. Measures to prevent, reduce, mitigate or compensate any adverse effects on the environment have to be assessed and mentioned as well as residual effects discussed.
Furthermore, information on the methods envisaged for monitoring the implementation of the SEA report have to be mentioned. The report should further contain recommendations for institutional strengthening, a communication strategy for disseminating report findings, a non-technical executive summary.
Describes the requirements for SEA review. Specifically: Who reviews the SEA? An independent body? Environmental Authority? Is the review approach similar to EIA review in the country?
The SEA guidelines mention an independent review of the SEA report, but no further info is given.
Participation in review
Are there any arrangements for participation in review? Who is involved? How is their involvement arranged?
Not specified in SEA guidelines.
What is the timeline given for the review of the SEA, in (working) days?
Not specified in SEA guidelines.
Informing and influencing decision-making
SEA and planning decision-making
What is the formal role of SEA in decision-making on the plan? Is SEA approval needed before a planning decision can be made?
The SEA guidelines do highlight the importance of a timely start SEA during the formulation of the PPP and that it has to be ensured that appropriate attention is paid to the outcomes of SEA and the measures recommended in the SEA report as well as to the outcomes of the consultations with authorities and the public. However, they do not specify procedures to ensure the integration of SEA into the planning decision. It seems that the guidelines rather suggest a case-by-case approach that determines the relation between SEA and the planning decision, as they provide a set of questions that can help to facilitate an understanding of how to ensure due consideration of SEA outcomes in the PPP formulation.
Recommendations for decision-making
How are the results of the SEA and participation translated into recommendations for decision-making on the plan?
Not specified in SEA guidelines.
Justification of decision
Does policy/programme/plan adoption decision-making have to be justified on the basis of the SEA?
Not specified in SEA guidelines.
Is there a requirement for implementation of decisions to be monitored? What is the role of SEA outcomes in this monitoring? What provisions exits for action to be undertaken if environmental problems occur?
The SEA guidelines mention monitoring as a formal step of the procedure, but do not give further details on it. They merely prescribe that the SEA report shall contain information on the methods envisaged for monitoring the implementation of the SEA report drafted.
Is there a formal requirement to evaluate the SEA? Similarly, to evaluate plan implementation before the next round of plan development? Are the two connected in this SEA system?
As for the monitoring, the evaluation of the SEA is mentioned as part of the SEA procedures in the SEA guidelines. Further information is lacking though.
Annual no. of SEAs
Gives an estimation for the number of SEAs that are produced annually in this country.
About 3 SEAs are produced annually.
Central SEA database
Is there a central database or library where information on SEAs is kept (i.e. where all SEAs are registered and/or copies are archived). If so, what is kept there and is this information publicly accessible?
There is no central database or library where information on SEAs is kept
Professional bodies relevant to SEA practice, such as SEA Associations, Planning Associations, etc are listed here.
Secretariat for Environmental Assessment in Central Africa (SEEAC)
P.O BOX: 30465 Yaounde, CAMEROON
Office 1: (237) 22 20 39 89
Office 2: (237) 22 01 57 41
Fax: (237) 22 20 39 89
Association pour la Promotion des Etudes d’Impacts Environnementaux au Rwanda (APEIER)
Sets out any ongoing training programmes (including professional and academic training) and major training events held in the past (with focus on recent events).
The ongoing five-year Decentralized Environment Management Project (DEMP, 2008-2013) is designed to strengthen environmental policy, planning and legislative capacity at the national level, to increase management capacity at the district and lower levels, and to empower people by promoting sustainable alternatives while protecting environmental resources.
The project included training workshops that incorporated key principles of SEA and served to build awareness for it.
Rwanda participates in the UNDP-UNEP Poverty Environment Initiative (PEI). From 2005 onwards various capacity building activities, trainings and workshops were held as part of this programme of which some were directly related to environmental assessment.