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WCS Fact Sheet for Zambia: Managing the threat of snaring to promote wildlife production and tourism development

Fact sheet #5, 6 April 2005

Background

Use of wire snares to capture and kill wild animals is a practice not uncommon to rural communities living in areas around Africa?s wildlife protected areas, especially communities affected by poverty and food shortages. Unlike the use of firearms, snares are silent and often go undetected, thus lowering risks of arrest by wildlife law enforcement officers. It is a passive, non-selective, and inexpensive way of killing wildlife. In contrast to firearms, which normally require considerable experience and skill, both men and women and even older children can easily practice snaring. When done on a large scale, snaring can be highly destructive, particularly to smaller-bodied animals, including the big cats. Deployment of wildlife scouts to search homes for possession of snares and patrol wildlife areas to remove them is costly and ineffective. This paper examines snaring as a wildlife threat to Zambia?s tourism and current efforts by Wildlife Conservation Society (WCS) and its collaborating partners1 to manage this problem through interventions of improved food security and increased access to fair market alternatives.

Prevalence of snares in Luangwa Valley

The incidence of snares encountered by safari clients while hunting in game management areas is a useful barometer of snaring prevalence. In addition, snare injuries to leopards and lions recorded by professional hunting guides are a useful indicator of snaring intensity. Based on interview data collected in 1999 among safari clients who hunted in four different safari concessions in Luangwa Valley, 36% complained about encountering snares during their hunts. In one particular concession, 3 of the 5 lions shot as trophy animals suffered from snare injuries (Cominos, pers. com.). Lodge operators promoting game-viewing tourism regard snaring as a major threat to lions, which become attracted to an animal already snared and increase the risk of becoming ensnared themselves where multiple snares were set at the same location.

Interview data with 448 residents living in these hunting concessions suggested that in 2000 as many as 57% of the households residing in or nearby areas with relatively high wildlife populations used snares on an average of 4.7 times per year, and on any given time, they would set approximately 6 snares in areas surrounding their villages. WCS selected these interviewees on the basis of their willingness to discuss their own use of snares without fear of reprisals by law enforcement officers.

Source of wires used for snaring

From a total of 5283 snares collected in Luangwa Valley, WCS undertook an analysis of each wire to determine type of wire and their possible source. 61.2% originated from winch cables and consisted of a variable number of interwoven wire strands of high tensile strength. The second most common wire used for snaring, representing 26% of the total sample, originated from bicycle tyres, which containtwo strands for securing the tyre on its rim. Other categories ranged from 1% to 6% and included building wire, electrical wire, electric fencing, and barbed wire. While bicycle wires represented an almost constant supply, based largely on the turnover rate of tyres by local bicycle owners. Winch cables, on the other hand, may represent a more limited and difficult source, since the majority of interviewees suggested these wires originated from mining operations elsewhere in the country.

Impact on wildlife numbers and tourism revenues

It is extremely difficult to quantify absolute numbers of wildlife lost from snaring for obvious reasons. However, results from the 448 residents interviewed on their own use of snares indicated WCS in 1999, 20 to 60% of the households in Luangwa Valley suffered chronic problems of food shortages, as influenced by such factors as rainfall, farming methods and crop varieties. A significant portion of these households, estimated to be 10% to 20%, relied on snaring to exchange game meat for farm-based foods. These figures suggested about 800 households, out of a total population of about 15,000 families, used snares, which contributed to an annual mortality of about 4500 animals over an area of about 12,000 km2.


Percentage contrast of safari clients who complained about encountering snares prior to and after interventions

Year

Chikwa

Chanjuzi

Chifunda

Mwanya

1999

15%

50%

17%

62%

2003

0%

0%

0%

30%

Species-sensitivity to snaring varies and likely depends on a species use of waterholes where snares are often set or animals that use regular corridors for their movements. Such sensitivities are probably responsible for the sharp local declines of waterbuck, hartebeest, roan, wildebeest and zebra in Luangwa Valley in recent years. The economic impact of these losses is directly related to reductions in safari hunting revenues due to lowered numbers of trophy quality animals, including the cats, and probably account for an underutilization of not less than two additional safari hunts per year. For the 9 concession areas in Luangwa Valley, this represents conservatively an annual loss of about $650,000 from gross safari revenues alone.

Interventions and impact on the snaring threat as a sustainable solution

In 2001, WCS launched a set of interventions built around a model referred to as COMACO2. The model targets food insecure and low income households with the opportunity to learn improved farming skills, access agricultural inputs, and benefit from low-cost, high-value transaction opportunities for farm-based commodities made available through a regional trading center. In exchange, households must organize themselves into producer groups registered with the trading center, based on their commitment to adopt improved land use practices and abandon snaring and other forms of destructive resource uses.

In three years, COMACO has recruited the participation of over 10,000 households and mobilized them into over 800 producer groups linked to a regional trading center in Lundazi through their local trading depots and has increased levels of household food security by approximately 68%. Compliance by group members to reduce their dependency on snaring, as well as illegal firearms for poaching, has yielded an unprecedented number of surrendered snares and firearms. Complimentary data from safari hunter questionnaires for four safari concessions suggest households have not replaced these snares with new snares. The results are presented below:

Year

Total snares collected

Total firearms collected

Coverage area (km2)

2001-2

6000

95

11,100

2002-3

8752

35

16,500

2003-4

17892

223

24,500

Total:

32644

353

Evidence provided by household surveys that compared use of snares in 2000 with 2003 showed a marked reduction of reliance on snares that correlated with a household compliance to improved farming practices and to increased levels of food security as improved markets became more available to producer groups.

Year

% h/holds using snares

Times snares used /yr

Average number of snares set

Estimated h/holds food insecure in core project area (11,100 km2)

2000-1

57%

4.7

6.1

>4000

2003-4

7%

2.4

4.8

Less than 1000

These results demonstrated that significant reduction in snaring is achievable by a farmer-based approach linked to improved farming skills and a marketing business design that offers local producers compelling incentives to remain committed to farming and improved land uses. Results also suggested this approach can sustain this reduced level of snaring with an annual saving of over 4000 wild animals as the COMACO business model becomes self-supporting through its regional trading centers. Results further suggested this approach can provide major windfalls for tourism by substantially increasing tourism revenues and tourism development opportunities by replacing household dependency on snares with more rewarding ways of meeting household needs that are conducive to increasing wildlife production. As wildlife numbers increase, however, the cost of living with wildlife will increase and the relative benefits of agriculture versus wildlife may upset the balance the COMACO seeks to achieve. A critical factor to help reinforce this balance is the willingness by the Zambia Wildlife Authority to increase economic incentives for producing wildlife.

1 WCS works with a consortium of partners, principally World Food Programme, Zambia Wildlife Authority, Food and Agricultural Organization, Programme Against Malnutrition, local District Governent authorities and the Ministry of Tourism, Environment and Natural Resources, to facilitate an approach that links food production with rural markets as an alternative to illegal use of wildlife.

2 COMACO stands for Community Markets for Conservation and Rural Livelihoods. For more details see WCS Factsheet #4 or inquire from WCS Lusaka office (254887) for a COMACO brochure on current programme results.

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