landscape diagnosis and perception

Current management principles (such as late mowing for export) are considered favourable and should be maintained. In order to preserve the mosaic of habitats and landscapes of the low-alkaline peat bog (northern sector), management actions should be considered to contain the cladia that is advancing on typical low-alkaline mire habitats. Localized sprigging could limit the expansion of the Marisque. In addition, management practices need to be correlated and refined with the ecology and location of the heritage species present.

In order to provide a regular diagnosis of the state of health of the site's environments and landscapes, a number of measures are implemented:

  • regular inventories of vegetation and flora by the Department's service providers to assess the effectiveness of management measures implemented
  • implementation of a new management plan as of 2023, based on an adapted reference framework, to target the best management measures
  • creation of a scientific council in 2023, which will meet regularly to discuss the site's evolution

Ecological studies carried out on the site in 2022 and 2023 determined that the ratio of mowing to grazing areas (considering the northern and southern parts of the site) was balanced and conducive to habitat conservation and the maintenance of vegetation diversity. In view of this favorable result, the current split between mowing and grazing is maintained.

With regard to the grazed southern sector, and considering that the overall grazing pressure reflects a punctual trend towards progressive closure (grazing refusals, woody rejections), it was deemed worthwhile to undertake the following actions in the short term:

  • selective clearing of undergrowth and crushing of overgrown areas, with export of cuttings;
  • introduce rotational grazing and consider enclosing certain areas.

Lastly, we need to monitor the evolution of the woody cover to justify whether or not it is appropriate to carry out one-off interventions, which can be costly and time-consuming.

Capacity building and informed decision-making for the monitoring of species

The implementation of the technical architecture and monitoring programme has ensured the availability of a big database of information both of the species and its environment. Data availability is key to ensure that park staff (managers, rangers, technicians, etc.) makes informed decisions when it comes to territory and species management strategies. Besides, the local design of the monitoring programme and the parameters within it, has increased the capacity of the park staff not only to manage it, but also to improve it and eventually apply it to the monitoring of different species and even other phenomena.

It is fundamental to ensure a co-design process, so that park technicians are not only the beneficiaries and end-users of the solution, but are also able to own and self-adapt the monitoring programme. To that end, an initial diagnosis of the capacities of the staff needs to be done, followed by specific training targeting the weaknesses that have been identified.

Currently, camera data is stored within the cameras themselves and technicians have to access and download the data manually. In order to fully implement this architecture, it is desirable to integrate a dual data storage device using both the device’s storage and a cloud service. The goal is to complete this integration to allow for an automatic process that reduces the time allocated to the monitoring process.

Characterization of the Reference Ecosystem and Definition of Degradation Levels

The objective of this building block is to provide technical teams with the biological parameters necessary to determine the current state of an ecosystem (level of degradation) and the desired state (healthy), in order to determine the appropriate restoration measures to be implemented in that specific ecosystem; for example, we will use the case of the Guatemalan dry forest.

The characterization of the ecosystem is done by documentary review and geospatial analysis, identifying the general-initial conditions of the ecosystem and its associations. Distribution / Climate / Soil Quality / Topographic Elevation / Flora Diversity / Fauna Diversity / Dasometric Characteristics of the Reference Ecosystems. For the dry forest, 3 associations were identified: 1) thorny scrub, 2) high dry forest and 3) riparian forest.

The definition of the levels of degradation is done by plot survey, comparing the successional states of the reference ecosystem with the dasometric characteristics obtained from the plots. In the case of the dry forest, three levels of degradation were identified: 1) pioneer succession, 2) secondary forest and 3) degraded forest.

  1. The existence of a policy framework that defines work in strategic forest ecosystems as a priority.
  2. The existence of policy instruments (conservation strategies, general forest management guidelines, etc.) oriented to strategic forest ecosystems.
  3. Groups interested in promoting or updating public policy instruments in strategic forest ecosystems where they implement actions.
  1. The quality of the characterization of the reference ecosystems and their levels of degradation will depend on the quantity and quality of documentary and geospatial information available; the generation of this information and the survey of plots in the field may require a lot of resources and time.
Measuring the Impacts on Ecosystem Services

The objective of this building block is to provide developers and implementers of ecosystem and landscape restoration projects with a tool that uses remote sensing, augmentation factors, and the integration of the two as a way to evaluate the effectiveness of restoration interventions on the ground.

To evaluate the line of impact of ecosystem services based on remote sensing, baseline data (baseline, management units and recent images) are collected and the differential between the initial and final year is calculated through: the definition of the increment tables, the normalization and adjustment of images, and the modeling of ecosystem services.

The increment factor approach is used for cropland and/or livestock where spectral indices derived from satellite imagery fail to accurately detect vegetation changes; and is calculated through: definition of baseline data, categorization of restoration practices and estimation of increment factors per implemented measure.

By executing this process, the area directly and indirectly impacted is available.

  • Have a baseline with the same variables and geospatial models to make credible and reliable comparisons over time.
  • Have a database of management units that clearly reflects the restoration actions that were executed in the field.
  • Implement a training and capacity building process with an assigned advisor, where doubts and uncertainties about methodological aspects and technologies to be used are resolved, which facilitates their adoption.
  • The databases that include the restoration measures in the territories should be reliable and preferably have been verified through supervision and control of data in the field.
  • If the developers and executors of restoration projects implement these methods in different areas, it is important to homogenize the variables, their treatment and the scale at which they execute them.
Elaboration of a Database on Restoration Measures

The objective of this building block is to provide developers and implementers of ecosystem and landscape restoration projects with a tool for collecting key information in the field to measure the impact of proposed restoration actions.

The steps for its implementation are:

  1. Survey of management units: provides complete information on the sites selected for restoration actions and includes; name and sex of the producer, correlative number and code of the management unit, administrative boundaries, geographic coordinates, area and legal status of the management unit, predominant land use and a photograph of the site.
  2. Survey of the management subunits: provides complete information on the specific restoration measures to be implemented in the selected sites and includes; the codes of the management subunits, coordinates and areas of the management subunits, current land use, future land use, restoration measures and practices to be implemented.

By executing this process, information is available that relates restoration actions to the improvement of ecosystem services in different parts of the landscape.

  • Incorporate new technologies and work distribution schemes to make field data collection and processing cost-effective.
  • Develop communication and performance protocols between office and field teams to collect quality data.
  • Have a supervision scheme that provides timely feedback to data collection and processing, while avoiding reprocessing.
  • The process of collecting management units is the most time-consuming part of this solution (estimated to be 2% of the project's execution cost), and therefore requires detailed and precise planning of the technologies to be used, the number of personnel required and the ways in which the data will be processed, as failure to do so in an appropriate manner may increase costs.
  • To take care of the processing and quality of the data, cross supervisions (internal personnel of the organization that is not linked to the project) or outsourced (external personnel that have been hired for this purpose) are required, which can identify inconsistencies in the databases and what has been executed in the field.
Ecosystem Services Baseline Construction

The objective of this building block is to provide developers and implementers of ecosystem and landscape restoration projects with a tool that uses remote sensing and geospatial data to determine the current state of ecosystem services and the sites where specific restoration measures can be implemented.

The steps to execute it are as follows:

  1. Preparation of baseline data: it forms a cartographic series that includes information on the project area, topography, climate, soil and forest cover.
  2. Hydrological and soil analysis: results in the water erosion map and the water infiltration map of the project area.
  3. Structural landscape analysis: results in the biological connectivity map of the project area.
  4. Integrated landscape analysis: results in the ecosystem services index and its map in different territorial management units.
  5. Generation of suitability indexes: results in 7 soil suitability maps to apply specific ecosystem and landscape restoration measures.
  • Have access to official geospatial information sources.
  • Implement a training and capacity building process, where doubts and uncertainties about methodological aspects and technologies to be used are resolved, which facilitates their adoption.
  • Have an advisor or mentor during the process; this facilitates the resolution of doubts or queries arising from the execution of the instruments; a single process of accompaniment is sufficient, as it develops a strong foundation for future replications.
  • It requires a technician with basic knowledge of GIS, since it requires access and manipulation of tools, data and platforms very specific to this sector.
  • The execution of the process is not time consuming, however, it requires time and exclusivity to perform it (more, if it is the first time it is executed); which are reduced with each new replication process.
Funded Projects

Following two funding calls, a total of 17 projects were selected. The projects represent a very wide range of different approaches and solution ideas for pursuing the Alliance's goals, depending on the respective context.

To increase the visibility of the projects and to foster knowledge exchange they are invited to present their ongoing work, intermediate goals and preliminary results to the Alliance community through posts on the website or at online events.

Sufficient funding is necessary to ensure long-term support and sustainable implementation of the project goals.

Continuous communication between those responsible for the project and the Alliance secretariat ensures the success of the project, the feedback of results to the community and thus added value for the community.

Adequate feedback from project partners can be challenging and requires good communication strategies.

Members Area

The members area is exclusive for registered members (individuals or organisations) of the Alliance. The membership is free of charge and gives you the chance to join forces for a common cause as well as connect, collaborate and partner with other members.

The Members Area serves as a platform for internal exchange, sharing of interesting articles, job opportunities and event dates as well as having access to video recordings of past events on demand.

  • maintaining the website and members area
  • it needs motivated and committed members who are willing to actively participate on the platform

At the beginning of the implementation, direct and regular contact with members is necessary to encourage them to post and interact with each other. Direct inquiries via email or reminders in the newsletter can help. Active support for posting from the secretariat is initially necessary but can be reduced over time.

Country packages

The aim is to establish practices, rules and/or standards to reduce risks to the environment, human and animal health in trade in wild animals and wild animal products in selected partner countries in global biodiversity hotspot regions. Among other things, risk assessments, the design of educational measures in different formats (digital and non-digital campaigns, training courses, etc.) and the scientific monitoring of the implementation of good practices (e.g. impact assessments) are to be promoted. The Alliance brings the relevant actors together across sectors and use concrete findings to formulate adapted regulations or or supports the institutionalization of relevant practices.

Existing political and GIZ structures, as well as other local partner organizations in the selected partner country.

Depending on the initial situation in the partner countries, you have to start at different levels. In some cases working together at the political level is possible, in other places it is more effective to implement the goals via a partner organization that already has experience on site and a network of local actors.

Working Groups

The International Alliance currently has 3 Working Groups, which are led by the members themselves and receive support from the Alliance Secretariat. Each Working Group is led by 1-2 chairs and the group meets every 6-8 weeks to ensure a continous work process.

We currently have the following Working Groups:

 

- Science Policy Interface (chair: Sue Liebermann, WCS)

Considering our core understanding of wildlife we want to infuse this understanding, based on scientific evidence, into international political processes.

 

- Transformative System Change: The Big Picture (chair: Alex D. Greenwood, IZW Berlin; Barabara Maas, NABU)

There are underlying fundamental obstacles to achieving the Alliances objectives and goals. Identifying and addressing these is the focus of this Working Group. 

 

- Evaluation/Effective Interventions (chair: Craig Stephen, One Health Consultant)

The aim is to gather good practices on effective interventions from Alliance members to enable learning and knowledge exchange across sectors and regions. 

The success of the working group depends on whether clear goals have been formulated, how committed and well- organized the chair is, how motivated the group members are and whether there is a continuous workflow.

Since most members already have very demanding full-time jobs, the time capacity of individual members may change over time. It can be challenging to ensure a good workflow and working atmosphere. Appreciation and understanding are of great importance in order to enable further collaboration.