Transboundary management options and external factors
Working with the coaches, the park authorities identify a list of factors that have strong potential influence on the ultimate objectives and that are at least partly beyond the control of park staff. They then narrow down the external factors to a focal set that has a high degree uncertainty about their magnitude and effects on the ultimate objectives. Next, park authorities develop two alternative scenarios representing possible future trajectories for the external factors. A status quo scenario assumes that system dynamics (i.e., external factors along with their impacts and effectiveness of management activities for achieving objectives) will follow the most likely future trajectory. An optimistic scenario assumes that system dynamics are more favorable than expected for achieving the objectives. To keep the participatory decision analysis feasible, additional scenarios (e.g., pessimistic) may be documented for future analyses. After listing possible management activities, park authorities independently assign a percent allocation toward each activity in a way they believe will most likely achieve the objectives under each scenario for external factors.
Initial lists of external factors and management activities were provided independently to ensure that no one park authority drives the final selection. During a workshop the core team developed a comprehensive influence diagram representing hypotheses about how ultimate objectives are influenced by management activities, resulting in a list of 9 possible activities. Joint discussions about percent allocations among activities led to adjustments to better reflect management realities.
The core team identified two external factors for inclusion in the decision analysis: 1) Agreement by Alpine countries in common politics concerning large carnivores. 2) Perceived level of competence of protected areas from perspective of stakeholders, allowing for their acceptance of carrying out park management activities and associated outcomes related to bear management. Eight of 10 respondents to the stakeholder-workshop questionnaire indicated that the external factors and possible management activities were clearly understood, although some suggestions were given to consider: 1) changes in stakeholder perceptions of large carnivores; 2) bear management in other parts of the population; 3) economic conditions for sheep breeding; 4) hunters lobbying for an open bear season; 5) adequate prevention tools for mountain pastures; 6) bear-related ecotourism should account for differences between parks in accessibility for tourists.
Selection of no-regret adaptation measures
Given the many uncertainties associated with climate change, political and community support for so-called ‘no-regret’ adaptation measures can often be higher than for alternative approaches whose (cost-)effectiveness depends on the degree of future climate change. The no-regret approach focuses on maximizing positive and minimizing negative aspects delivered by EbA, and selecting actions that yield a range of benefits even in the absence of such change. In the case of the Kamen green-blue-corridor, the ecological improvement of the stream in combination with disconnecting the storm water from surrounding properties was determined to have positive impacts regardless of whether rainfall will increase in the long-term or not. Should rainfall intensify and become more frequent, flood risks will be reduced; if temperatures increase in the summer, the stored water will benefit the mircroclimate. Regardless of climate, however, the EbA measures can be considered as ‘no-regret’ as they create amenity and recreational benefits for the community and visitors, increase awareness levels, contribute to the EU Water Framework Directive and biodiversity conservation, and reduce water discharge fees for local inhabitants.
In order to gain political and public support for such measures, it is key to have sound scientific evidence of the potential benefits which can be created regardless of climate change and to compare these to other approaches. The outcomes of such comparative analyses can be disseminated via targeted awareness raising campaigns to highlight the potential environmental, societal and economic benefits and thereby foster greater recognition of the value of EbA, increase public support, and lead to
A range of obstacles can serve as potential barriers to implementing no-regret EbA actions, such as (i) financial and technology constraints; (ii) lack of information and transaction costs at the micro-level; and (iii) institutional and legal constraints (as outlined on the European Union’s Climate-Adapt platform). It is thus important to conduct assessments of the (cost-)effectiveness of the no-regret option as well as of other available measures in order to facilitate informed decision-making and steer appropriate communication campaigns. In Kamen, such comparative data was gathered and presented in group meetings and bilateral discussions to community members who were considering decoupling their rainwater from the sewage system. Given the reliance on private citizen support for a successful implementation, it was of particular importance to highlight the ‘no-regret’ character of the EbA measures alongside the personal benefits which could be expected.
Engaging private citizens to implement adaptation measures
Successful implementation of EbA sometimes necessitates the involvement and support of private actors in cases where the measures are to take place on their land. This can create a challenge as the process of convincing individual stakeholders to participate in implementation activities often requires significant time investments, financial resources, and public outreach efforts. In the case of Kamen, it was necessary to determine the value of decoupling private citizens’ rainwater from the sewage system and then to convey this information in a convincing manner to those involved. Two public information meetings were followed by one-on-one planning sessions in which a technician visited individual homes and drafted catered solutions for disconnection that met the needs of each citizen. Furthermore, financial incentives were provided to the residents in the form of expenses per decoupled square meter to motivate participation.
The project’s success can be credited to the participation and engagement of private citizens. Their support for decoupling rainwater from the sewage system emerged from a combination of several factors: outreach and awareness raising activities, public funding, voluntariness, provision of targeted and bilateral on-site expert advice, and a reduction in fees for disconnected households.
Given the high importance of citizen support and participation in the project, significant efforts and resources were invested in motivating participation. The approaches taken underscore the value of investing time in one-on-one sessions, in which information and arguments for participation are tailored to each stakeholder. As a consequence of these efforts, most of the property owners in the area were aware of the project of the need to adapt to climate change, and understood the value of their contribution as single actor. This has led the residents to be highly accepting of the implemented EbA measures and develop a sense of ownership, as well as to be open towards and even encourage the pursuit of further adaptation initiatives in the future in order to reach climate change adaptation goals and produce additional co-benefits for themselves and the environment.
Securing sufficient funds for a multi-purpose EbA solution
As this solution serves various goals and meets several objectives, it was possible to secure sufficient funding from diverse parties, domains and funding bodies to cover the entire implementation of the project. Innovative financing approaches can also act as ‘self-sustaining’ and generate funds during the course of the project to fund some of the foreseen activities.
Given that the solution serves various goals, funding was able to be secured from a range of parties, sectors and sources. In the case of the creation of Lake Phoenix this included funding for water management from the water board; funding for ecology from the ecological funding program by the federal state; funding for urban development from etc. The water board, for instance, provided the amount of money that was already budgeted for the construction of a flood retention basin.
Establishing the diverse benefits provided by a solution is an important step in the planning process, as it highlights the various sectors and stakeholders who can potentially be involved in and benefit from the solution. Drawing attention to the potential benefits, and underlying this with a sound scientific evidence base with which to approach these parties, can facilitate the successful generation of funds from a range of sources.
Synergistically combine various interests and goals for the EbA solution
In order to find an EbA solution for e.g. the development of an area in which multiple actors have an interest in, it is important to synergistically combine various interests, ambitions, challenges and goals.
A crucial factor for the realization of Lake Phoenix was the successful linking of various problems (flood risks; abandoned brownfield site; underprivileged part of the city) and goals (flood retention; river restoration; increase of attractiveness of the city, etc.) to gain support from a range of actors. To this end, the lake was designed to serve as a biodiversity hotspot, flood retention basin, and recreational area. Most significantly, it increased the
Achieving multiple objectives required compromising, for example between ecological objectives (i.e. size of the lake and natural areas) and economic priorities (i.e. land being available for real estate development). As a result of a common will to succeed and a number of group and bilateral meetings between key stakeholders, these compromises could be reached. Interviewees also highlighted that the actors’ good relations and belief in the project helped find solutions, just as it helped to settle discussions concerning upcoming additional costs and risks. The (historical) role and position of the water board as a mediator was important in this respect. The realization of Lake Phoenix was furthermore facilitated by favorable timing, being that the Emscher conversion coincided with the abandonment of the brownfield site.
Villager Trail Mapping; capturing local knowledge
Government staff and surrounding villagers are able to communicate with each other when a common language on geographical features is established. Villagers surrounding the protected area have been brought up with the local knowledge of the area which includes local names and characteristics. Capturing this information is done in three repeated steps. The first step is to organize village meetings using general topographical maps in which the villagers indicate trails inside the NPA and names of areas, rivers/streams, hills etc. Where possible the villagers indicate areas they are controlling. The second step is to train teams of rangers (villagers & PA staff) to use GPS receivers and to have them walk all trails collecting location specific names and boundaries with GPS coordinates. The third step is the creation of updated maps with all trails and with location-specific names. The information on this map is then verified in a village meeting. These three steps may be repeated several times. The resulting maps are then used in discussions on zoning and village area delineation which determine the area for Village Rangers to patrol and which rules apply.
As there is very little known about the Hin Nam No in general, there was no objection by the responsible ministry to start collection of data from the bottom up. The villagers are very willing to share their knowledge of the area and lively discussions amongst villagers erupt when different perceptions or names are known. Returning with updated maps creates a lot of understanding from both sides, and direct map updating in the village meeting with high resolution imagery shows the villagers the importance of their knowledge.
The initial topographical maps used in village meetings should be accurate and show rivers and hills/cliffs with the names in the local language (and script). Maps printed on vinyl sheets allow villagers to write and erase with white board markers which supports discussions as labels can be changed. It is difficult for villagers to determine boundaries between locations. Especially for areas like forests, the boundaries are difficult to indicate as the boundaries are known only on the trails, not further afield. Some areas are limited by physical features (rivers, hills/cliffs) and thus with remote sensing estimations can be created but these need verification. Therefore several rounds of trail mapping, updating and meetings are required as villagers and government staff learn from each other which type of information is required for a common understanding. The resulting maps should be discussed with different groups in the village to ensure agreement and common understanding by all.
Village Ranger System
There are 18 villages that have traditional land rights inside the park boundaries. First 4-5 rangers per village were selected by the community based on their willingness to become rangers, knowledge of the area and having time available. The first teams were set up and trained to start villager trail mapping. Payment fee for biodiversity monitoring and patrolling was agreed through negotiations and based on a fair compensation for the hard and dangerous work of hiking in the mountains. The division of the park in village responsibility areas designates the village ranger working areas. Due to the different sizes, terrain and threats, some villages indicated the need for many more rangers and involvement of village militia or police. Now 110 villager rangers have been trained in use of GPS equipment and in the recording of sightings in coded booklets. They make regular trips into the park to record wildlife and threats (monitoring) and are involved in patrolling for law enforcement. The patrol frequency is adapted with the incoming information. As the village rangers know the area well, they are willing to go into very remote places and in very difficult circumstances where other rangers usually do not venture.
Identification and acceptance of the limitations by government: agreement to fill the gap left by government of people for patrolling. A system that government could support in future: as cheap as possible but an effective patrolling system; no ranger stations and part time workers. Use limited government resources as effectively as possible as staff does not know the area well and do not want to work under remote and difficult circumstances; make use of local knowledge and hardened people for ranger activities.
The system of village rangers depends on the willingness of all villagers to uphold the rules that they have established and agreed upon, as for the village rangers it is not possible to arrest their neighbors. Therefore it is important to have a separate ranger team focused on law enforcement from the government/outside. Village rangers only work in their own village managed area as trust between villages needs to be built. In the Hin Nam No the village ranger teams always include village militia or police who are authorized to carry arms which is a requirement to stop well equipped poachers. Training on monitoring, apprehension and other tasks needs to be done regularly. Clear processing of violators and support for poaching camp raids needs to be established. Feedback sessions are an important tool for exchange of information and improving effectiveness.
SMART data collection tool
SMART is a ranger based data collection tool specifically for managing patrolling activities. As it is a data collection tool for spatial data, the database was re-designed to not only serve the patrolling needs but also the wildlife monitoring and location data gathering needs. Training was given to government volunteer staff to work with the software and adapt the database, and to rangers on the use of the data booklet. Trials were done and the database and data booklet adapted to requirements from rangers and researchers, i.e. small size booklets, wildlife per category (indicator, key, hunted). To be able to collect data systematically and report important features to management, a tool like SMART is ideal. As the data gathering is done by staff with limited reading/writing capabilities, we simplified and coded the booklet, with the codes on the front and back of the booklet. The data entry (and reporting) can be done by few experienced staff. As rangers stay in the field for up to 6 days and electronic data gathering equipment does not have this kind of battery power, a more sophisticated system is not possible. For more sophisticated geographical analysis and mapping, the data is transferred to a GIS system.
The tool is promoted by major players in the conservation world and as such is seen by the partner organizations as a tool that is acceptable. The tool is free and thus, besides training, no extra costs are necessary for software licenses. The very limited amount of data before the adoption of SMART and the lack of qualified staff to manage the previous software made the change easy. It is possible to transfer data from an old system into SMART.
There needs to be an absolute minimum of one highly trained staff member who is responsible for entering the data, analyzing the results and creating the reports for management. More people is better as regular sharing of the database prevents data losses. Training of the staff responsible for SMART takes time as it is complex. Providing information to management creates awareness and results over time in further requests for information. This motivates those involved in data gathering (the rangers), analysis and reporting (PA staff). It is necessary to be flexible at the start of the usage of the tool as to be able to adapt to the data gathering needs. This requires several rounds of updates and trials; the database should be kept flexible. Training of rangers on the data booklet needs to happen several times and regular feedback of patrolling results increases effectiveness.
Public rewards for best actions
All work is recorded in photos and videos and disseminated on social media. The best actions and practices are awarded in public events. The association will meet at its General Assembly and each member will vote for a person to be named the volunteer of the year. The person with the most votes will be publicly awarded and reported in local and national media.
Existence and partnership with a local community Radio station.
By publicly rewarding a person you motivate them and inspire others to follow the same example. You have to make sure the process is clear and fair to avoid any discontent.
Community beach patrols
The beach patrols occur at night to collect data and make sure the female turtles are not disturbed and slaughtered. The patrols are undertaken by 2 to 4 community persons groups which are led by a more experienced person of the Caretta Association. We collect data such as animal length, width, presence of external parasites, injuries, and localization of the nest. The data is collected and entered in a form to produce a further report and publication. Our constant presence on the beach is also a message to move away the poachers.
Proximity of the community to the beach. Aroused curiosity to see a sea turtle laying eggs.
This hands-on activity provided the community a different perspective and developed a sense of belonging. Before that they should all go through a training in order to make sure the presence of not experienced people does not become a threat.