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HUNT · EU FP7 research project

Social-ecological modelling

Social-ecological modelling for sustainable hunting

The management of hunted species is a complex process driven by interactions between the population dynamics of the species, the decision-making and behaviour of stakeholders and uncertainty at various levels of the management process and the natural system.

Harvest management models often do not explicitly incorporate the social processes underlying harvester behaviour, and are based on the use of a “best” management solution to achieve a single objective. Where the system is relatively simple and harvesters abide by rules, such as in some recreational hunts in the developed world, this may not be problematic. However, in complex systems, with multiple stakeholders and severe uncertainties, it is generally difficult to provide a single best harvest policy. Instead, there is a need to find robust approaches that meet management objectives under a range of potential states of the world.

One approach that aims to do this has gained considerable ground within fisheries science; Management Strategy Evaluation (MSE), uses simulation models within an adaptive framework that enables the comparison of alternative strategies in a virtual world under multiple and often conflicting objectives. We have expanded the MSE framework to include individual harvester decision making to make it more suitable for terrestrial conservation.

MSE has five major advantages over standard approaches to providing management advice:

Best practice

Uncertainty needs to be at the centre-stage in the modelling process. Uncertainty plays a fundamental role in the dynamics of ecological and economic systems, in our measurement and understanding of these systems, and in the devising and implementation of rules to control harvesting

Hunting is a crucial contributor to people’s livelihoods in many parts of the world. Management often works against the short term economic interests of those who depend on resources by decreasing the harvest or closing areas to protect its natural resources. The welfare of resource users, securing ecosystem service provision and integrating conservation and development is of key importance for social-ecological modelling. This means that the incentives and decisions of people who depend on the resource must be included in the MSE model.

It is crucial to develop systems understandings collaboratively and with a range of stakeholders, not just scientists, and explicitly model trade-offs between different objectives, and the perspectives of different stakeholders.

 

Outlook for future studies

There is a need to engage with, and overcome, the reluctance of social and economic disciplines to engage with a quantitative approach to institutional and cultural complexities

Engaging with stakeholders early, and in a participatory manner, is crucial for success but scientific researchers are not always equipped with the tools, contacts and experience to do this. Engagement should be done before the modelling starts, and throughout the modelling process, so there is a need to be organised about this, and develop strong collaborations from the start.

The MSE approach can readily be integrated within an adaptive management framework so as to guide learning in the real world, but this needs a substantial amount of time (several years) which we did not have on this project.

 

Case studies

Mountain nyala in Ethiopia

The mountain nyala is an endangered ungulate endemic to Ethiopia and is hunted for trophies by mostly foreign hunters. We have a good understanding of the decision making process used to set the quotas but we have less understanding of the monitoring process and the error in the abundance estimates. Life history parameters, such as fecundity and survival rates are missing for mountain nyala which adds additional uncertainties to the sustainable management of trophy hunting. Our models clarified the relationship between the length of the monitoring period, the uncertainty about key parameters (including poaching and abundance estimation) and the flexibility of the hunting quotas (how quickly they should change in response to new information). We developed a simple harvesting rule that is robust to changing circumstances and allows managers to increase both their quota and the nyala population. However, this is dependent on engaging local people more, so as to reduce the external threats posed by poaching and habitat encroachment.

 

Lynx in Norway

Since 1994 the lynx population in Norway has been subject to quota hunting, as a mean to control population size but also to allow recreational harvest. In fact, Norway is unique in Europe by managing lynx as a normal game species. Still, the lynx quota harvest is often associated with much controversy also in Norway, due to the charismatic nature of large carnivore and their high conflict potential with livestock husbandry. As steps to increase the understanding of ecological and social factors affecting lynx harvest and lynx population dynamics in Norway we have used a wide set of tools. In particular, we have focused on the factors affecting the relationship between management decisions (quotas) and actual harvest off-take, on the appropriateness and accuracy of the current monitoring scheme, as well as the direct effects of harvest on lynx population dynamics. As time lags in the monitoring process in the past seems to have caused unstable dynamics, a statistical prognosis tool forecasting the lynx population (with associated uncertainties) one year ahead under a given harvest scenario has been developed and is likely to reduce this latter challenge by giving wildlife managers a formal tool to use in setting quotas. Further developing models under the MSE framework would allow simultaneous consideration of the uncertainties in both the ecological and management process. This would be a valuable next step and much of the knowledge is now available for such a model to be developed.

 

 

Partridges in Spain

The main uncertainty for partridge management in Spain is the relationship between the number of captive-reared birds released, the sustainable quota for shooting and the estimated abundance of wild birds. Good data exist on the uncertainties surrounding monitoring of abundance and the relationship between estimated abundance and realised hunting. However, the decision making process on how many to release, how to set the quota and the role of hunter demand in driving management practices is less transparent and less well known. This needs further investigation using social science methods. We are developing a model that will demonstrate the need for research into these key uncertainties, and will enable us to test different combinations of releases and quotas to enhance estates' sustainability.

 

Lions in Africa

Lion hunting in Africa is an opportunity to generate revenues for conservation but recent data show a declining trend in lion numbers across Africa due to trophy hunting. Most hunting areas lack good monitoring data on abundance; in fact often there is no estimate of lion population size that can be used to set hunting quotas. Using the MSE framework we developed a new approach to quota setting, based only on the data which are easily available to hunting companies; the time it takes to find and kill a trophy lion. Using a simple decision rule, we simulated the sustainability of quotas under a range of uncertainties, including the possibility of hunters misidentifying lion age and so killing younger lions by mistake. This rule is very robust, and so would be a useful component of hunting rules, complementing the existing restrictions on hunting younger lions. This approach is applicable to any circumstance where hunters kill a single animal on a hunt (i.e. most trophy hunting).