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Forests Sourcebook - HCV Resource Network

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decision-making processes. SEA may focus on environmental<br />

impacts or its scope can be the integrated consideration<br />

of all three dimensions of sustainability: environmental,<br />

social, and economic. SEA may be applied to predetermined<br />

PPPs or be integrated into PPP formulation, and may<br />

engage a broad range of stakeholders or be limited to expert<br />

analysts. SEA can be conducted in a short time frame or<br />

over a long period. Some SEA may consist of a quick analysis<br />

while others require detailed analysis. Environmental<br />

assessment can be the starting point of an SEA but SEA can<br />

also be fed into an existing process, such as policy analysis.<br />

Furthermore, SEA could be a finite, output-based effort, or<br />

a more continuous process that is integrated within institutional<br />

processes.<br />

SEA provide a flexible approach. From an operational<br />

standpoint, SEA can provide a flexible approach that varies<br />

according to the complexity of the decision-making<br />

process. At one extreme, it focuses on impact assessment<br />

and, at the other extreme, it centers on institutions and<br />

governance (see chapter 5, Improving Forest Governance).<br />

Along the continuum that lies between these two, the decision-making<br />

process is more significantly influenced by<br />

political bargaining and the interaction of different interest<br />

groups and constituencies. Consequently, only a balanced<br />

institutional framework can capture and effectively take<br />

into account the rights and concerns of small communities,<br />

minorities, and stakeholders affected by environmental<br />

degradation. Therefore, as PPPs move up in the decisionmaking<br />

hierarchy for contributing to sustainability in<br />

development processes, SEAs focus more on building institutional<br />

capacity and strengthening governance than on<br />

assessing impacts.<br />

Impact centered SEA and institution centered SEA.<br />

When political economy factors and political bargaining are<br />

not important in defining a PPP, the SEA is rooted in EIA<br />

experiences and methodologies involving technical<br />

processes. Some observers have called this the “impact-centered<br />

approach to SEA” 2 because it focuses primarily on predicting,<br />

preventing, and mitigating adverse environmental<br />

and social impacts, similar to EIA of projects and activities.<br />

Conversely, in PPPs significantly influenced by political<br />

economy and political factors, the SEA is rooted in policy,<br />

institutional, and governance analysis, involving multistage,<br />

nonlinear, iterative processes. Because of this focus, it can be<br />

called an “institutions-centered approach to SEA.”<br />

Although both types of SEA can be used in forestry PPPs,<br />

impact-centered SEAs are largely adequate in programs and<br />

plans for reforestation, extraction, and processing of wood<br />

and nonforest products, and watershed protection. Typically,<br />

an impact-centered SEA consists of the following four<br />

stages 3 :<br />

■<br />

■<br />

■<br />

■<br />

First is establishing the context for the SEA, in which<br />

potential impacts are screened, the SEA’s objective is set,<br />

and stakeholders are identified.<br />

Next is implementation of the SEA. It begins with establishing<br />

the scope of the SEA and the participatory<br />

approaches to bring in relevant stakeholders. Like EIA, in<br />

this stage baseline data is collected, alternatives are identified,<br />

and measures to mitigate adverse impacts and<br />

enhance opportunities are proposed. This stage includes<br />

an assessment of the institutional conditions needed to<br />

effectively implement the SEA recommendations. These<br />

results are circulated publicly during a consultation<br />

process and a final report is prepared.<br />

The third stage is informing and influencing decision<br />

making. It overlaps to some extent with the second phase<br />

because presentation of the draft and final reports are<br />

key points to influence decision makers. In this stage,<br />

decision makers become aware of the options open to<br />

them, the likely effects of particular choices, and the consequences<br />

if they fail to reach a decision.<br />

The last stage is monitoring and evaluation of the SEA.<br />

Institutions-centered SEA is mostly appropriate for<br />

forestry policies, in general, and forestry reform, in particular.<br />

Forestry reform induces changes in property rights,<br />

institutional reform, and adjustment in the incentives<br />

regime to manage and use forests, and thus is likely to<br />

engender significant environmental and social effects and<br />

opportunities (see note 5.2, Reforming Forest Institutions).<br />

In this situation, SEA can only be successful if it influences<br />

the reform and policy process, which requires SEA to be<br />

fully integrated into the decision-making process. The SEA<br />

team should work along with the forestry policy team<br />

responsible for the reform. It should provide inputs on the<br />

potential environmental and social effects of the proposed<br />

policies and be responsive to the requirements of policy<br />

makers and planners when policies are being formulated<br />

and implemented. In box 6.18 a program SEA for the implementation<br />

of forestry policy in Cameroon presents key<br />

components of an institutions-centered SEA in the context<br />

of an impact-centered SEA. In box 6.19, an institutions-centered<br />

SEA on the Kenya Forest Act is described to illustrate<br />

how the SEA was integrated with the decision-making<br />

process and World Bank activities.<br />

NOTE 6.4:ASSESSING CROSS-SECTORAL IMPACTS: USE OF CEAS AND SEAS 241

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