You are currently browsing the tag archive for the ‘community involvement’ tag.

One aspect of community involvement in a conservation project is that members of the community may be involved in activities that contradict, or seem to contradict, the project’s aims – this may include things like fishing, hunting, and culling activities. The idea is to get people to either abandon these activities or adopt a more sustainable method of carrying them out, and the way this is done is through community incentives or benefits.

In Lucy Emerton’s paper on community benefits in Africa, she summarises the general approach to providing community benefits:

In order to achieve the joint ends of conservation and human welfare improvement such projects and programmes have followed a common approach to generating economic benefits for the people who live in wildlife areas. In combination with other forms of local participation in wildlife management, benefits have tended to be provided by returning a proportion of the revenues earned by the state from wildlife back to them through indirect benefit-sharing arrangements and grass-roots development activities mainly the provision of social infrastructure such as schools, water supplies and health facilities.

It’s important to consider that wildlife may have a serious cost to communities which in turn leads to culls. The International Gorilla Conservation Programme refers to this as “human-wildlife conflict”, which includes crop raiding by gorilla, elephant, buffalo, etc. Where this kind of conflict is a problem, building a school is not going to much of a deterrent for culling, because the original conflict remains a problem. Other types of benefit can be implemented instead with some success, provided there is significant community participation to determine the best course of action. The IGCP’s page on community initiatives says this:

In DRC and Rwanda, for example, with support from IGCP, park staff and local communities have been building a dry stone wall (one meter high and one meter thick) around the park perimeter. Building the wall has been a positive step toward reducing conflict between the park and the community as buffalo no longer raid crops and people are able to cultivate field closer to park boundary; thus increased crop production and increasing income. The record harvest in areas already protected by the new wall has encouraged local communities to extend the project.

There was a recent story that was a prime example of blatantly inadequate community involvement (not to mention wildlife assessments) in decision making, where a 4-year $575,000 USAID project to improve the lives of coastal communities in Kenya resulted in the provision of plastic fishing nets, rather than the traditional hook and hand lines (against the requests of the local fishermen’s associations). The plastic nets have been damaging the ecosystem, killing wildlife and coral. That’s quite a lesson right there.

In this month’s Landscape Research there’s an article by Monica Lorenzo Pugholm about potential community benefits for Jamaican fishermen, which largely fall under the category of “alternative livelihoods” (which actually means a career in tourism – see my post on the dangers of ecotourism here). The result was that the benefit may have made sense in terms of financial income, but occupation comes down to a lot more than money, and ultimately the switch from fishing to tourism did not constitute a sufficient benefit.

The actual fiscal value of an area in terms of natural resource products may be huge, so don’t be fooled into thinking there isn’t a substantial financial benefit in fishing to begin with. The Guinea Current Large Marine Ecosystem, for example, has been evaluated in the last month (by authors from UNIDO, BDCP, IGCC, and the University of Nigeria) at US$49,941.4 million, or over US$20,081 million not including offshore oil. In theory, the value of an area’s natural resources should be an incentive in itself, in that unsustainable harvesting of resources will result in a catastrophic boom-bust dynamic. Unfortunately, that’s a detached and simplified way of looking at it, because in reality fishing less (for example) may not be an option depending on other community or personal pressures, particularly when people are living in poverty. A person has certain requirements for feeding themselves and their families, and it is not enough to say “your requirements are too great.” You need to find not just other avenues of meeting those requirements, but better avenues.

Along a similar vein, I’ve been reading this article in Environmental Conservation by authors from the Wildlife Conservation Society and the University of Kent about the India Eco-Development Project at Periyar Tiger Reserve in Kerala, India (summarised on Nature Data):

The Periyar Tiger Reserve, India, is supported by the India Eco-Development Project (PTR-IEDP), an integrated conservation and development project (ICDP) funded by donors. The project has been internally evaluated as successful, although out of the US$6million received, only 43.2% went to community-based conservation activities. When an independent survey of 180 people (half of whom had benefited from the PTR-IEDP, half of whom had not) was carried out, 71.1% of those who had benefited said their attitude to conservation was not changed by the project, and of the 55 community benefits only 36.4% were still being used.

Unfortunately I can’t see beyond the abstract because I don’t have an athens login or whatnot, but I would love to know what exactly those community benefits were, and why 63.6% of those benefits are no longer deemed beneficial.

The reason I started thinking about community benefits was that I saw the very engaging film The Age of Stupid, which is about climate change and why the switch to green energy pronto is so important. Among other things, it features a group of middle-class English people protesting a wind farm because it will ruin their view and damage house prices and be noisy (despite being right next to a go-kart track), although when pressed they claimed to be very concerned about climate change. The general consensus from those I knew was that the protesters were stupid and selfish, and actually I was inclined to agree, but I think this attitude is not helpful and only succeeds in isolating the green energy movement from local community members. What would be more helpful would be to consider the specific grievances and by collaborating come up with solutions, such as adapting the turbines’ design or offering tax breaks for existing homes near turbines, or some previously unthought-of marvel. Could a community benefits project be applied to middle-class rural English communities? Can’t hurt to try.

The Canary Islands sound very interesting. You can access some GIS data via Google Earth, thanks to the Canary Islands Spatial Data Infrastructure.

As well as 50% of their vertebrate species (Juan et al., 2000), 21 non-migratory vertebrate species, and 7 birds (Blanco and Gonzalez, 2002), endemic fauna of the Canary Islands include 5 bird of prey subspecies: the Canarian Egyptian Vulture (or Guirre), a Common Buzzard, a Eurasian Sparrowhawk, two Eurasian Kestrel subspecies, and a Barn Owl. The Islands are also home to Barbary Falcons and Ospreys (Palacios, 2004).

The Canarian Egyptian Vulture is an endangered bird now restricted largely to Fuerteventura and to two territories on Lanzarote. The subspecies declined rapidly due to collisions with power lines, poisoning, and increased tourism, and in 2000 there was estimated to be only 25-30 breeding pairs (Donázar et al., 2002).

The European Commission’s LIFE (Financial Instrument for the Environment) project for Spain planned to introduce measures to protect the Canarian Egyptian vulture by October 2009:

A 50% reduction in the adult mortality through collision with power lines will be attained by introducing corrective measures in the island’s power lines. An increase of 20% in the breeding success will be achieved through reinforced surveillance of nesting areas. Surveillance and awareness raising measures will be implemented with the aim to reduce the use of poison. Finally, to avoid the potential threat of famines, three controlled middens will be created with the collaboration of local livestock breeders.

Middens are also known as ‘vulture restaurants’, and are basically areas with a constant supply of carcasses (provided by humans) so food availability for the birds is never erratic. This would hopefully encourage breeding and improve survival, thereby increasing the number of birds and helping to establish a sustainable population. Sounds like a great example of a simple and easily implemented conservation method, right?

Sort of.

In an article in this January’s Animal Conservation by a team from CSIC (Spanish National Research Council) including a member of the team that originally described the species in the first place (Donázar et al., 2002), it was found that, when artificial ground-nesting birds‘ nests were placed along lines 200m to 34km from vulture restaurants (as summarised on Nature Data) “of the 67% lines predated by carrion-eaters, 90% of nests were attacked.”

It’s never simple, is it?

At least it’s predictably never simple. The complexities of population dynamics are mind-blowing, but by anticipating that there are complexities and learning more about the ecosystems, reserve management continually gets more effective.


Blanco JC, Gonzalez JL, 1992. “Libro rojo de los vertebrados de Espana.” (Red List of the vertebrates of Spain) Ministerio de Agricultura, Pesca y Alimentacion, Madrid, Spain. (via Donázar, 2002)

Cortés-Avizanda A, Carrete M, Serrano D, Donázar JA, 2009. “Carcasses increase the probability of predation of ground-nesting birds: a caveat regarding the conservation value of vulture restaurants.” Animal Conservation, 12(1): 85-88, doi: 10.1111/j.1469-1795.2008.00231.x (CSIC, full pdf here)

Donázar JA, Negro JJ, Palacios CJ, Gangoso L, Godoy JA, Ceballos O, Hiraldo F, Capote N, 2002. “Description of a new subspecies of the Egyptian Vulture (Accipitridae: Neophron percnopterus) from the Canary Islands.” Journal of Raptor Research 36(1): 17–23 (CSIC, full pdf here)

Juan C, Emerson BC, Oromí P, Hewitt GM, 2000. “Colonization and diversification: towards a phylogeographic synthesis for the Canary Islands.” Trends in Ecology and Evolution 15: 104-109, doi: 10.1016/S0169-5347(99)01776-0 (Universitat de les Illes Balears)

Palacios JC, 2004. “Current status and distribution of birds of prey in the Canary Islands.” Bird Conservation International, 14:3:203-213, doi: 10.1017/S0959270904000255 (CSIC)