Abstract:The paper analyzes the conflict between illegal and legal exploitation of wildlife species in an East African context. In the model there are two agents, an agency managing a national park of fixed area and a group of local people living in the vicinity of the park. The park agency has the legal right to exploit the wildlife, while the local people hunt illegally. Because of the property rights, the park agency has incentives to invest in the stock of wildlife, while the behaviour of the local people is steere… Show more
“…9 See Clark [5,6] for a two-patch model of optimal spatial exploitation where harvests can be instantaneously adjusted in the case of relative density-dependent dispersal systems. Using the Clark [6] formulation, Tuck and Possingham [24] investigate optimal management in a two-patch, sink-source system with no economic heterogeneity, and Huffaker et al [10] and Skonhoft and Solstad [21] investigate optimal management in a two-patch setting for terrestrial species. Janmatt [11] finds qualitatively similar results to ours when studying the optimal spatial management for a northeast Atlantic clam fishery.…”
“…9 See Clark [5,6] for a two-patch model of optimal spatial exploitation where harvests can be instantaneously adjusted in the case of relative density-dependent dispersal systems. Using the Clark [6] formulation, Tuck and Possingham [24] investigate optimal management in a two-patch, sink-source system with no economic heterogeneity, and Huffaker et al [10] and Skonhoft and Solstad [21] investigate optimal management in a two-patch setting for terrestrial species. Janmatt [11] finds qualitatively similar results to ours when studying the optimal spatial management for a northeast Atlantic clam fishery.…”
“…It also creates considerable tension over wildlife in the national parks that border the less productive farm areas. 3 See also Shulz and Skonhoft (1996), Skonhoft and Solstad (1996), and Skonhoft and Solstad (1998), on the welfare of the communities. Communities are passive in this model, receiving the revenues of the property shares and the burdens of the wildlife interactions, which take the form of intrusions.…”
“…Previous studies examining the enforcement of resourceuse rules have tended to concentrate on the users' incentives (for example fishers or poachers; Leader-Williams & MilnerGulland 1993;Skonhoft & Solstad 1996;Damania et al 2005). However, the success of enforcement also depends crucially on monitors' incentives to carry out their duties (Mookherjee & Png 1995;Mesterton-Gibbons & Milner-Gulland 1998;Robinson et al 2010).…”
SUMMARYMany conservation interventions seek to change resource users' behaviour through the creation and enforcement of rules. Their success depends on changing the incentives of potential rule-breakers and those who monitor and enforce compliance. Project implementers may use payments to encourage monitoring and sanctions to deter rule breaking but there has been little research to examine the effectiveness of such approaches in promoting compliance with conservation rules. The effects of payments and sanctions on poaching in a hypothetical community-based conservation project were investigated using an individual-based model incorporating individual heterogeneity and a realistic range of behaviours. Individuals could choose to poach, monitor others' behaviour, or 'cheat' (claim a fee without actually monitoring behaviour). They could also invest in avoidance to reduce their probability of being detected breaking rules. Community-level outcomes emerged from individuals' choices and strategic interactions. The model demonstrates that payments and sanctions can interact strongly with one another and that their effects depend on the economic context in which they are applied. Sanctions were more reliable than payments in reducing poaching and, in some circumstances, payments produced perverse effects. It is thus important to consider individual-level heterogeneity and strategic decision-making when designing interventions aimed at changing human behaviour.
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