Research Group 1: Evolutionary Ecology
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GAME-MEAT HUNTING

1. Illegal game-meat hunting in the Serengeti ecosystem and its impact on the spotted hyaena population

2. Optimality model: costs and benefits of game-meat hunting in the Serengeti

 

Illegal game meat hunting in the Serengeti ecosystem and its impact on the spotted hyaena population

Prior to the establishment of the Serengeti National Park and associated protected areas in northwest Tanzania, game-meat hunting within the Serengeti ecosystem was a component of the lives of many local communities. The establishment of the Park effectively outlawed all hunting activity within the Park, whilst hunting in the protected areas adjacent to the Park as only legal if conducted under license.

Game-meat hunting provides both protein and cash income. These and related benefits have drawn people to villages close to the park boundary, causing a rise in human population density well above the regional average.


Serengeti ecosystem (Natural Resource Modeling, 2000, p. 154)

The unregulated exploitation of wildlife and the destruction of habitat threaten many species and these destructive processes are accelerating as human populations increase. The level of illegal offtake by game-meat hunters has caused a dramatic decline in herbivore population in certain areas within the Park and associated protected areas and game-meat hunting can be considered to have a major predatory impact on both resident and migratory herbivores.

As a majority of game-meat hunters use the unselective hunting method of wire snares tethered to woody vegetation, populations of non-target species are also affected.

   
rock hyrax und lion with wire snare

At the onset of the dry season, the migratory herds start their trek from the short-grass plains in the south-east to their dry-season refuges in the north and west of the Park, close to the villages who hunt within the Park. Owing to their commuting system, spotted hyaenas from clans throughout the Serengeti regularly hunt in areas with snare lines during the dry season. Using longterm data from individually known hyaenas, the impact of snaring on the Serengeti spotted hyaeana population could be assessed. The alarming result of this analysis revealed that about 8% of the population is killed each year by snares. Death due to snares is the most important mortality factor acting on the Serengeti hyaena population. Dependent cubs belonging to the mothers that are snared are doomed to die of starvation, as hyaena mothers typically will only suckle their own cubs.


spotted hyaena with wire snare

 

 

Optimality model: costs and benefits of game-meat hunting in the Serengeti

From the originally hyaena concentrated view of the game-meat hunting, Prof. Hofer and collegues from the Natural Resources Institute in Great Britain developed a research program that investigates the causes of game-meat hunting and assesses the impact of poaching on the entire herbivore population of the Serengeti.

It concerns in particular models which accurately predict the spatial distribution of the hunting activity. Hence, such models are of practical, strategic use and could support the park administration when making decisions about the placement of new ranger posts or how best to direct law enforcement patrols. Secondly, optimality models from the behavior ecology with considerable success are used, which were originally developed for the solution of other problems.

This allows the insight that basic research and interdiciplinarity for a deepened understanding of applied problems are important and the linkage of both most interestingly. Optimality models can help to answer the following questions: How profitable is hunting? How are the costs and benefits of the hunters distributed? Where is hunting most likely to occur? Where should we expect to see the biggest impact of hunting on resident herbivores?

The problem of which location to choose for hunting is similar to the task that many animals face when searching for food (i.e. the smallest input with the highest yield). We constructed such a model of the spatial distribution of economic costs and benefits of illegal hunting during the late 1980s and early 1990s where costs and benefits were defined in monetary terms.

Costs included capital investment in hunting weapons, WR, and the opportunity cost of hunting, WO, both held to be constants; and two spatially variable components, the logistic effort of traveling to hunting areas, WL, and the penalties incurred if arrested, WP. Benefit was the expected income from the sale of meat from resident wildlife species.


Spatial distribution of the modeled profitability of hunting in USD
in the protected area of the Serengeti

The model suggests: (1) WR is the most important cost. (2) WL is the second most important cost and likely to determine the spatial distribution of hunting activity if hunters seek to minimize costs. (3) WO and WP are of minor importance, the former because alternative sources of income provide low pay, the latter because the overall chance of being arrested is low. (4) WP exceeds WL only in areas close to the boundary of protected areas. (5) Although resident wildlife contributes only a minor share of illegal offtake compared to the migratory herds, hunting resident wildlife is profitable in 68% of the area. This suggests that hunting of resident and migratory wildlife is highly profitable and may explain why the utilization of the target populations has become increasingly unsustainable.