Cost-benefit analysis
Alternative adaptation options were analyzed via the Marine InVest tool to identify costs and benefits of these approaches. Costs were incorporated directly into the scenarios and InVEST. This included the costs of implementation of adaptation options combined with any associated costs to ecosystem services quantified by our models, and benefits represented by the positive return in ecosystem service values quantified by our models. Local experts helped in reviewing the selected ecosystem services and adaptation options. A technical report was developed on the activities.
The models had the capacity to effectively quantify the potential costs and benefits of climate change and alternative adaptation strategies to lobster fishing and coastal protection, and alternative adaptation strategies to tourism and carbon storage and sequestration. The ecosystem service models provided a useful framework for tackling a complex set of issues within limited timeline.
Using storylines, spatial scenarios for Integrated and Reactive adaptation approaches, three models for ecosystem services, model for seawall protection from storms, information from the literature, and stakeholder expertise, we were able to effectively quantify the benefits of adaptation options in terms of revenue from lobster and tourism, carbon storage and sequestration, and avoided damages to coastal infrastructure. Outputs from models are relevant to Belize’s decision-makers, the public and private sectors, as described in building block 5. This CBA approach helped to clearly assess the costs and benefits of alternative adaptation options in an efficient way. Standardizing both costs and benefits, such as ecosystem services, in monetary values enables cross-sector decision-making and allows for a more complete economic assessment of options.
Community-based ecotourism
Mangrove custodial association members are trained as guides for ecotourism activities as a possible alternative source of income. Visitors learn about locals’ regular activities such as fishing, catching crabs or collecting molluscs. They are then given the experience of preparing and consuming the mangrove’s bounty.
- Organisation with committees - Support from governments or corporations to train guides - Collaboration with tourism sector - Advertisements Institutionalised management is the key to connect tourism service providers with customers. Publicity is needed to attract tourists as well as resources like boats for visitor’s transport in the different concession zones.
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Technical Assistance (TA)
Unlike Social Marketing, the Technical Assistance (TA) is based on more personal interactions with the fishers at the fishing group level (cooperatives or associations) or at the individual fisher level. This allows the issues to be addressed with more detail and depth, although larger groups of people are not reached. The overarching goal is to promote fishers´ support for conservation actions (e.g., creation of FRZ, adoption of sustainable fishing practices). Technical assistance tools are targeted towards building capacity in coastal communities and removing technical barriers, emphasizing leadership among fishers to improve the management of fisheries resources. Examples of technical assistance activities include one-on-one conversations, fishing trips, fisher exchanges among sites, formal training in specific fishing methods through workshops and courses, informal training, meetings with the authorities, follow-up with administrative and legal processes (e.g., fishing concession/permit renewal) and providing organizational materials (e.g., file cabinets, blackboards, etc.).
• High level of technical experience and skills of implementing partner allow deeper and more detailed TA interventions with fishers. • Well designed, implemented and analyzed formative research supports the definition of thematic areas for TA. • Partnerships with government agencies and NGOs to add human and financial resources and give fishers assurance that their effort is acknowledged. • Target audience participation in the design and future implementation of TA activities to generate ownership and contribute to reducing the resistance to the campaign effort.
Technical Assistance interventions help the campaign address issues identified in the Barrier Removal step, but interventions are not necessarily limited to that stage in the process. Despite the differences in the context of each campaign site, defined by the conditions of the country and the fishing industry, very similar thematic areas were identified for each TA strategy. Building trust with the fishers is a primary step for all TA activities. Those activities which involve as many fishers as possible generate ownership in fishers and facilitate the adoption of behaviors. Moreover, fishers are empowered to follow up on the agreements derived from each activity, improve their self-organization, establish agreements internally or with third parties to publicly reaffirm and guarantee their collective decisions, and promote their participation in activities that impact the fisheries management decision-making process.
Climate adaptation scenarios
Climate impact hypotheses were translated into quantitative relationships and data layers for use in the InVEST ecosystem service models. Adaptation strategies were selected based on outcomes for ecosystem service provisioning with a set of four climate adaptation scenarios tested. In selecting the most appropriate adaptation strategies, we drew on existing research with stakeholders in Belize that identified the ‘best options’ for sustainable development, adaptation, and mitigation of climate change in Belize, and looked at these under three management scenarios.
• Existing strategies from climate development-partner funded efforts were the basis for discussion. The strategies had a focus on linkages between climate adaptation, mitigation and sustainable development (triple-wins) in the coastal zone. • Literature review and focus group discussions were used to refine the list of strategies, to identify measures that are: feasible for Placencia to undertake; to map and value; and clearly responsive to climate impacts.
In some cases, there were insufficient data or understanding of the nature of the relationships between the climate change variable and ecosystem service to model robustly. As a result, we were only able to model climate impacts for two out of the four service models: lobster fishery and coastal protection. Limited time and human capacity restricted our ability to model sea level rise impacts on coastline retreat at a fine scale (e.g. more precise modeling of mangrove distribution and land loss needs finer resolution bathymetry data). The resolution of existing bathymetry data for Belize is quite poor, as it is for much of the region, and the limited timeframe of this work (10 months) precluded the pre-processing of bathymetry data. We got spatial results about changes in ecosystem services from climate change and development factors but we could not identify particular groups most vulnerable to these changes due to data gaps.
Develop, discuss and evaluate PA management recommendations
Recommendations from the preparatory steps of the Convention-Check are given to the management agency, then are evaluated after an appropriate period of time, to assess their impact and largely address management effectiveness. Steps in this building block include assessing and quantifying the number of changes of measures/activities on management, administrative and legislative levels, assessing the causality between recommendations and evaluating the quantified changes in a qualitative way. Recommendations are provided to administrative and legislative bodies as well as to the PA in particular. Recommendations concern changes in legislation, administrative regulations as well as in particular in practical management decisions. One recommendation was for example to work on bats and now these species are among the flagship species of the park.
Working closely with relevant organizations and societies such as the Thaya Valley National Park Society offers a productive way to assess relevant changes.
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Mangrove reforestation
Shrimp farmers are obligated to develop and implement a mangrove reforestation plan within their production area; they pay community members, often women, to garden the mangroves, including re-planting.
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Documenting and sharing the success story
This building block focuses on documenting and disseminating results so that the experience can be captured and replicated elsewhere. Sharing and disseminating successful project results can encourage other interested parties to conduct site visits to observe the project first hand and meet the people involved. This kind of peer to peer learning can often be the first step towards replication. Documentation can also be used as a powerful advocacy tool to create leverage for greater commitment to waste management policies at regional and national scales. Documentation can be in many different formats ranging from a brief project summary or personal testimonies from the people involved, to powerful images that show the project in action or short film clips that can be embedded in websites and shared on social media etc. The greater variety of visual documentation the project has, the greater influence it can have on decision making processes related to waste management (or any other issue of concern). Documentation of results also plays an important role in the review and evaluation phase so that project leaders can identify the contribution of each building block to the overall outcome.
Ability to document project results in a visually appealing way, access to dissemination pathways.
One of the most powerful media for sharing results is through personal testimonies on film. However, this can be expensive if done through a professional media house. However, there is plenty of free, online digital editing software available that can be used to produce a film clip ‘in-house’ for a fraction of the cost.
Community-based tourism: economic incentive for conservation
After initial assessments to determine what could be the most appropriate livelihood activities that would further encourage conservation action in the landscape, the Community-Based Tourism (CBT) plan was developed and the community was trained to run the programme. The CBT programme comprises promotion of home-stay units, home restaurants for food, a cultural group to showcase Monpa art and culture, organized treks through the conserved areas and provision of trained service providers (guides, managers, cooks, porters, etc) to support all of these. The community has sought to include as many families as possible in the programme so as to ensure spread of programme benefits. The CBT in Thembang, one of the project villages, is now in its seventh year with revenues increasing four-fold since inception, amounting to 23,000 USD as of March 31, 2015. The CBT was successfully replicated in other project villages based on biodiversity values. In similar line, WWF-India is also diversifying income generation activities to other forms of rural enterprises for conservation impacts. Recently, it facilitated the process to establish a unit to manufacture Tibetan incense stick with available forest resources in Pangchen valley.
Baseline information is collected on various parameters including family income and energy usage to decide suitable activities. The baseline report also helps to assess our intervention impacts and • Awareness/ conservation education programmes for larger community to enable a thorough understanding of what CBT entails. • Community willingness to actively participate, acquire the knowhow and implement the required actions. • Unique selling points in terms of cultural and biodiversity values to attract people for the CBT model to be sustainable.
A detailed participatory assessment is very crucial in the implementation of any income generating activities (IGAs). The IGAs should be developed jointly with community members rather than in a “top down approach” and encourage communities to take up activities they are familiar with. We encouraged IGAs that have direct linkages with the nature conservation and culture. Participatory planning and ensuring people’s participation is very important in livelihood interventions. For conservation impacts, there should be a direct link between nature conservation and livelihood initiative. There are some economic incentive programmes that have been successful in raising per capita income of the community, but have had very little conservation impact, or sometimes conservation status even deteriorates. Therefore, identification of a proper set of IGA and enabling people’s participation is the key of success.
Insertion in the community
Building trust between MarViva and the Community Councils of each community has taken more than four years before the development of the Communication Collective. Creating an association between the Collective and the Foundation has been based on the respect for the interests, decisions and role of the Community Councils. This partnership has allowed the insertion of the Foundation in the communities where it is positively seen as a strategic partner. This integration has been strengthened by successful previous processes where communities have perceived the benefits of partnership and the "fair play" by the Foundation.
Establish personal relationships with community leaders to meet and discuss one to one the vision of these community leaders. Create participatory methods in making decisions that develop an acceptance and identification with the decisions taken.
Invest time to create a strong partnership with communities is essential before achieving successful experiences. This relationship requires time and constant interactions with community leaders. It is important to establish clear rules for this interaction from the very beginning. The respect by the Foundation for community decisions and the avoidance of taking the leading role were elements that helped create that trust.
Monitoring and evaluation
Monitoring and evaluation (M&E) are vital components of every Pride campaign, without which assessment of the effectiveness of the intervention cannot be conducted. M&E takes place in every component of the Theory of Change (please refer to the building block 'Theory of Change' for a brief description of each component). Monitoring keeps score on how effectively capacities are built, how effectively social marketing efforts lead to changes in behavior, and if those behavior changes lead to desired conservation outcomes. Monitoring basically tracks every component of the ToC. M&E of knowledge, attitude, interpersonal communications and behavior change is based on pre and post campaign surveys of the fishers, while threat reduction and conservation results use specific protocols validated by experts.
• Having a local monitoring partner or consultant is key to develop timely baseline data and monitor threat reduction and conservation results. • As with any project or program, having adequate and sufficient funding is key. Teams may rely on existing human, equipment, facilities, and financial capacities to reduce costs. • Sites with long term tradition of monitoring are better suited to produce a solid baseline of biological monitoring indicators.
An important lesson related to biological monitoring is when there is the possibility of having a two person team for each campaign, a Campaign Manager (CM) and a Fisheries Fellow (FF). This arrangement allows for one person to concentrate on the fisheries technical aspects, including the necessary time for biological monitoring. The level of involvement of the FF in the monitoring component depends on his/her personal inclination towards science. There are examples where the FF devoted a considerable amount of time and effort to conducting monitoring and analyzing data, while others did not participate at all. This could improve with a clearer definition of the FF’s role in regards to biological monitoring. Having a person dedicated to monitoring in Rare’s team ensured all fisheries campaigns had baseline and post campaign impact data.