manual for social impact assessment of land-based ... - Forest Trends

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Table T2: Detailed Qualitative Assessment and Rating of the Seychelles Marine Project (SEYMEMP–GEF) TOC Component Qualitative Assessment Rating Outcome 1: Marine ecosystems understood Outcome 2: Measures addressing marine degradation introduced ID: Research and monitoring methodology integrated into ongoing initiatives/ institutions ID: Research & monitoring capacity built in Seychellois institutions ID: Mitigation strategies integrated and funded by existing structures Intermediate State: Ongoing research informing decision making and scaling up of actions to protect the marine ecosystems Outcome 1 and 2 were well achieved by project end. Detailed research activities (focusing on ~60 protected and non protected coral reef sites and turtle nesting areas) enabled a good assessment of the impact of the 1998 coral bleaching event and established good monitoring baselines. Coping mechanisms were introduced including the management of coastal wetlands, the deployment of mooring installations and the control of plague organisms on coral reefs. The ecosystem monitoring protocols adopted by the project proved statistically stronger, simpler and more time efficient than previous approaches and have since been adopted more widely (e.g. by the GEF ASCLME project) Research findings have fed into Status of Coral Reefs of the World 2008 (Global Coral Reef Monitoring Network) Turtle Action Group formed at project close and continuing standardized tagging mechanism to understand turtle movements and nesting patterns New research now looking at spawning aggregations and fish behavior to assess whether the MPA network is big enough Since project completion, the Wetlands Unit (now Waterways Management Section) has classified all wetlands and is using GIS mapping as an integral part of EIAs The research studies were contracted to Reefcare International and independent consultants, resulting in limited capacity built in country The Marine Unit was established in the conservation division of the MET to have responsibility for marine research, but since project closure it has not been active; lacking funds and expertise (only one person) and it is likely to be closed down in 2009. Whale shark program continued by MCSS following project closure The enactment of strict guidelines (Wetlands Policy 2005) has enabled Wetlands Unit to police illegal activities (dumping/ reclamation) and ensure major new developments comply with guidelines and undertake EIAs. However, capacity is insufficient to enforce guidelines at household level. Wetlands taskforce grew to 40 staff mandated to remove waste (removing 1.5 tonne/ week in Victoria) and maintain wetlands, but under recent restructuring this work is being contracted out under one or two supervisors The initial plan that MCSS monitor the managers of marine areas (i.e. SCMRT/MPA and private entities) to maintain the mooring installations has not worked. SCMRT/MPA is due to take on this responsibility? Mitigation measures to control marine grazing was stopped following project closure Ecosystem understanding, especially the extensive research on turtle nesting areas (Dr. Mortimer) has informed decision making: E.g. the identification of new refugia for protection led to government decision not to allow increased fisheries in sensitive areas Enforcement of wetland regulations by Wetlands Unit is reducing risk of landslides and waste entering marine ecosystem, but techniques (such as grills) have not been scaled up from original project pilots Socio-economic valuation work (by Dutch consultant Herman Cesar) has not been utilised, nor integrated into development planning/ EIAs Marine Parks Authority (SCMRT/MPA) is not using research & monitoring findings to inform management of marine national parks. This is attributed to the Marine Unit being established in the conservation section of the DoE rather than the SCMRT/MPA where the current lack of scientists has restricted their activities. Source for Tables T1 and T2: Reproduced with permission from GEF Evaluation Office & Conservation Development Centre. 2009. The ROtI Handbook: Towards Enhancing the Impacts of Environmental Projects. Methodological Paper #2. Global Environment Facility: Washington DC. http://www.thegef.org/gef/node/2096 2 2 1 2 2

T2.4 Participatory Impact Pathways Analysis (PIPA) Designed to assess impacts in the water and food sectors, the Participatory Impact Pathways Analysis (PIPA) is based on a participatory workshop in which the project stakeholders make a set of explicit assumptions of how the project impacts will be achieved (http://www.prgaprogram.org). As with the 'Open Standards' approach, this should ideally be undertaken at the project design stage. Description of Method The main steps in PIPA are set out in Figure T9. PIPA starts with a 3 day participatory workshop involving 3-6 groups of 4-6 people. Participants undertake the following activities: Problem tree and identification of outputs (day 1) The problem tree uses a linear cause and effect logic to understand the project rationale and what needs to change. The branches of the problem tree end when it has identified a problem that the project should tackle. Once identified, these ‘determinant problems' help define the project outputs needed to solve them. Outputs are defined as "things the project produces that others beyond the project use" (Douthwaite et al., 2008). ‘Vision of success’, 'network maps' and strategies (day 2) The cause and effect logic of the problem tree is balanced by a 'network perspective' in which impacts are the result of interactions between stakeholders or actors. The idea of network maps is to model the relationships between stakeholders in the 'with' and 'without project' scenarios. Participants first construct a 'vision of success' in which they try to imagine what different types of stakeholders will do in the future assuming that the project is successful. Categories of stakeholders include: project implementers; politically influential people and organizations who could help (or hinder) the project; the users of project outputs (or 'next users'); and groups who will work with the 'next users'. Participants then draw up a 'now network map' showing current key relationships between the stakeholders, and a 'future network map' showing how the stakeholders need to link up or work together to achieve the project vision – this should show the required changes in attitudes, networks, etc. Participants then identify the strategies, activities and outputs needed to bring about the required changes. Outcomes logic model and an M&E plan (day 3) On the third day, the participants combine the cause-effect descriptions from the problem tree with the network maps into an 'outcomes logic model' (Table T4). This describes in tabular form how the various stakeholders need to act differently for the project to achieve its vision. The rows describe the required changes in each set of stakeholders' knowledge, attitude, skills and practice, and the project strategies to bring these changes about. The resulting changes are defined as outcomes. Social Impact Assessment of Land-Based Carbon Projects (1.0) – Part II | 18

T2.4 Participatory Impact Pathways Analysis (PIPA)<br />

Designed to assess <strong>impact</strong>s in the water and food sectors, the Participatory Impact Pathways<br />

Analysis (PIPA) is <strong>based</strong> on a participatory workshop in which the project stakeholders make a set <strong>of</strong><br />

explicit assumptions <strong>of</strong> how the project <strong>impact</strong>s will be achieved (http://www.prgaprogram.org). As<br />

with the 'Open Standards' approach, this should ideally be undertaken at the project design stage.<br />

Description <strong>of</strong> Method<br />

The main steps in PIPA are set out in Figure T9. PIPA starts with a 3 day participatory workshop<br />

involving 3-6 groups <strong>of</strong> 4-6 people. Participants undertake the following activities:<br />

Problem tree and identification <strong>of</strong> outputs (day 1)<br />

The problem tree uses a linear cause and effect logic to understand the project rationale and what<br />

needs to change. The branches <strong>of</strong> the problem tree end when it has identified a problem that the<br />

project should tackle. Once identified, these ‘determinant problems' help define the project outputs<br />

needed to solve them. Outputs are defined as "things the project produces that others beyond the<br />

project use" (Douthwaite et al., 2008).<br />

‘Vision <strong>of</strong> success’, 'network maps' and strategies (day 2)<br />

The cause and effect logic <strong>of</strong> the problem tree is balanced by a 'network perspective' in which<br />

<strong>impact</strong>s are the result <strong>of</strong> interactions between stakeholders or actors. The idea <strong>of</strong> network maps is<br />

to model the relationships between stakeholders in the 'with' and 'without project' scenarios.<br />

Participants first construct a 'vision <strong>of</strong> success' in which they try to imagine what different types <strong>of</strong><br />

stakeholders will do in the future assuming that the project is successful. Categories <strong>of</strong> stakeholders<br />

include: project implementers; politically influential people and organizations who could help (or<br />

hinder) the project; the users <strong>of</strong> project outputs (or 'next users'); and groups who will work with the<br />

'next users'.<br />

Participants then draw up a 'now network map' showing current key relationships between the<br />

stakeholders, and a 'future network map' showing how the stakeholders need to link up or work<br />

together to achieve the project vision – this should show the required changes in attitudes,<br />

networks, etc. Participants then identify the strategies, activities and outputs needed to bring about<br />

the required changes.<br />

Outcomes logic model and an M&E plan (day 3)<br />

On the third day, the participants combine the cause-effect descriptions from the problem tree with<br />

the network maps into an 'outcomes logic model' (Table T4). This describes in tabular <strong>for</strong>m how the<br />

various stakeholders need to act differently <strong>for</strong> the project to achieve its vision. The rows describe<br />

the required changes in each set <strong>of</strong> stakeholders' knowledge, attitude, skills and practice, and the<br />

project strategies to bring these changes about. The resulting changes are defined as outcomes.<br />

Social Impact Assessment <strong>of</strong> Land-Based Carbon Projects (1.0) – Part II | 18

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