Demographic characteristics of respondents.
Abstract
This chapter examines the ecological effects of bushmeat extraction activities/methods and utilization of wildlife resources in the study area. It also highlights the perception of rural dwellers on the abundance of wildlife resources in the past 10 years as well as suggesting solution to this impending danger of depletion. Two different methods were used. The first method being stratified sampling method was used to investigate the activities involved in the extraction and utilization of wildlife resources, while the other method used a questionnaire to investigate the local people’s perceptions on the abundance of wildlife resources. Results showed that gunshots were the most used (32.4%) of all the methods of extracting bushmeat in the study area, followed by the use of snares (25.5%). However, 86% (n = 86) of the respondents admitted that they consume bushmeat, while only 14% (n = 14) claimed otherwise. Buying bushmeat from markets and hunters ranked highest 55% (n = 33) among the methods of getting bushmeat in the study area, followed by the method of indirect hunting 30% (n = 18). Respondents claimed that bushmeat was occasionally consumed 38.1% (n = 37). Furthermore, 88% (n = 86) of the respondents agreed that there has been drastic change, while only about 12% (n = 12) objected to the marked difference in wildlife abundance in the park in the last 10 years. Note that 53% (n = 49) of the respondents agreed that wildlife resources in the study area have been depleted. The perception of the communities’ members on the establishment of community-based wildlife management program in the area is significant (0.013*) at 0.05 level. The study revealed high level of hunting activities resulting from the use of unsustainable hunting methods, high demand for bushmeat, and lack of capacity to control hunting in the park. Lack of adequate attention to the role of bushmeat utilization as an important contributor of local livelihoods by development agencies, nongovernmental and intergovernmental organizations, and national governments contributes to the unsustainable hunting of bushmeat in tropical forests. Finally, to achieve the levels of protection necessary, habitat preservation therefore remains the key criterion for any conservation program, for without sufficient quantity and quality of habitat there will be no viable wildlife population to protect.
Keywords
- biodiversity
- national parks
- conservation
- bushmeat
- hunting
1. Introduction
Forest-living people have few alternative sources of protein and income than bushmeat [1–3]. Thus, hunting of wildlife may be locally intense, and may threaten the entire populations or even species [4]. Over 160 species are endangered in West-Central Africa [5]. Uncontrolled hunting practices are only pushing these species closer to extinction. Overhunting caused the recent extinction of Miss Waldron’s red colobus monkey. Several other primate species are soon to follow [6]. Up to date, it is not known exactly how many species have been eradicated and gone into extirpations due to excessive and uncontrolled hunting. However, it is evident that many species will become extinct if hunting pressures continue at their current level.
Nonetheless, the intensity of bushmeat exploitation may fluctuate even locally due to eventual perturbating events: for instance, the spreading of Ebola virus was accomplished by a considerable reduction of bushmeat consumption in West Africa [7]. High bushmeat demand has been recorded for west and central African countries (Liberia [8], Ivory Coast [9], Ghana [10, 11], Cameroon [12], and Gabon [13, 14]) and for the Congo Basin as a whole (e.g. [15–18]). Previous studies have demonstrated that bushmeat consumption is an integral part of the livelihood, both as protein requirement and important source of supplementary income, but it is also of a major sociocultural importance [19]. Overexploitation of various species has been found to be the key reason for forest wildlife declines in Africa [20]. Exploitation as a phenomenon is noted to be on the increase as a result of growing human populations, improved access to undisturbed forests, changes in hunting technology, and scarcity of alternative protein sources [21–23]. Fa et al. [24] subsequently enunciated that bushmeat depletion in the Congo Basin in real existence and supply may lead to 81% drop in less than 50 years, if the current rates of harvest continue, which may further aggravate the dramatic increase in protein malnutrition. It is therefore noteworthy to submit that overexploitation and utilization of wildlife for bushmeat and protein sources in West and Central Africa is a serious palaver which can degenerate to local, national, or worldwide extinctions of targeted species, with saddening ecological and economic consequences. Sustaining different species of wildlife both for future economic and social reasons therefore becomes a vital point of direction if the stability in the ecological system must be sustained.
The Oban hills forest area of Cross River in Nigeria is a very important conservation region with unique biodiversity, with many endangered species being confined to this region. While bushmeat trade and marketing have already been subject to research, the extent to which wildlife resources and bushmeat utilization and extraction as well as the effects on the stability of the ecosystem is yet to be substantiated. This work specifically examined the ecological effects of bushmeat extraction and utilization of wildlife resources on the stability of the ecosystem. It also highlighted the perception of rural dwellers on the abundance (increasing or dwindling) of wildlife resources for the past decades when compared to the present time as well as suggesting solution to this impending danger.
2. Location and description of the study area
Cross River National Park, the first tropical rain or moist forest national park in Nigeria, is located in Akamkpa Local Government Area of Cross River State, Nigeria. It was created by Act Nos. 36 and 46 of 1991 and 46 of 1999, respectively. It covers an area of approximately 4000 km2 and consists of two divisions:
The study was carried out at the Oban Hill Sector. The
3. Methods of data collection and analysis
Two different methods were used. The first method was used to investigate the activities involved in the extraction and utilization of wildlife resources while the other method (the use of questionnaire) was used to investigate the local people’s perceptions on the abundance of wildlife resources. Oban Sector of Cross River National Park is divided into two (west and east) ranges. Five villages were purposively selected from these two ranges within the Oban Sector–Aking/Osomba (05°25'67"N, 08°38'10"E), Ekang/Esang (05°40'00"N, 08°49'00"E), Ekuri (05°21'25"N, 08°26'24"E), and Ifumkpa (05°31'56"7N, 008°17'30"4E) based on their proximity and being on the periphery of the park. Eight transects of 2 km each were laid in each of the four land-use types (core, buffer, farm fallow, and plantation) in the study locations at 1000 m intervals using a stratified sampling techniques and placed 2000 m apart to avoid animals from being detected on two neighboring transects with effective study area of 64 km2[27, 28]. The transects were modified as recommended by Buckland et al. [27] and were traversed for 40 consecutive times to allow for more encounters of activities of wildlife resources extraction and utilization including spent cartridges, match box, used carbide, wire snares, traps, hunting camps, hunters encountered, and gunshots heard within 10 m of both sides of the transects were recorded. Spent cartridges found were collected but wire snares were destroyed. Purposive (judgment) sampling was used as the second method to select a sample of the local respondents and study communities [29]. Purposive sampling was used due to the proximity of these villages to the park. A total number of 100 respondents from the selected villages (Aking, Ekang, Esang, Ekuri, and Ifumkpa) were interviewed, all living within a 10,000 m distance from the park boundary. The method was an interview-administered questionnaire. The questionnaire included both open-ended and fixed-response questions. The questionnaire was designed to evaluate the perceptions of local people toward wildlife resources abundance within the study area. Education and demographic information, including gender and age, were obtained from each respondent. All interviews were conducted by a research assistant who was the Assistant Range Head. Oral interviews were carried out during the day in the local language (
4. Data analysis
Data gathered from the questionnaire were grouped and summed by response category. The responses were recorded on a data sheet and later transcribed into English and entered into a Microsoft Excel 2010 database as well as Statistical Package for Social Sciences version 19 for Windows (IBM SPSS Inc, Chicago, USA). Where multiple responses were possible on an open-response question, data are presented as the percentage (%) of respondents giving each response, and may sum to 100%. Pearson moment correlation coefficient and descriptive statistics were also used.
5. Result presentation
Data were generated from five locations–Ifumkpa community 22 (22%), Ekuri community 19 (19%), Esang community 22 (22%), Aking/Osomba community 18 (18%), and Ekang community 19 (19%). The sample comprised of 73 males (73%) and 27 females (27%). About 32% (
The study revealed that 44 (47.0%) of the respondents are principally secondary school certificate holders, 37 (39.4%) are primary school leaving certificate holders, while 7 (7.4%) of the total respondents are diploma and teacher certificate holders while 1 (1.1%) of the respondents are first degree holders. Also, 4 (4.3%) of the respondents do not have formal education.
From Table 2 it can be seen that gunshots were the most used (32.4%) of all the methods of extracting bushmeat in the study area. This was followed by the use of snares (25.5%). Other activities of extraction include hunters’ trails (12.8%), hunters’ camps (2.9%), and spent cartridges found (19.5%).
From Table 3 it can be seen that 86% (
Figure 2a shows that 88% (
Figure 2b shows that 53% (
Table 4 shows the relationship between the communities’ members’ perception on status of wildlife resources in the study area and the establishment of community-based wildlife management program in the area. The result shows that both variables are significant at 0.05 level (2-tailed).
6. Discussion
6.1. Demographic characteristics of respondents
Table 1 shows that young people participated more (86.0%). It also shows that majority (68.0%) of the respondents have their abode near the forest meaning that they do not have to trek much before getting into the park. This nearness then shows the peoples’ dependence on the park resources. However, the result indicated that majority (73.0%) of the respondents are male (Table 1). Figure 1 reveals the educational background of the respondents. Most of the respondents (47.0%) were secondary school leavers, followed by primary school leavers (39.4%). This shows that education influences their attitude and perception toward wildlife resources utilization
S/N | Variable | Frequency | % |
---|---|---|---|
1 | |||
Ifumkpa | 22 | 22.0 | |
Ekuri | 19 | 19.0 | |
Esang | 22 | 22.0 | |
Aking/Osomba | 18 | 18.0 | |
Ekang | 19 | 19.0 | |
Total | 100 | 100.0 | |
2 | |||
Male | 73 | 73.0 | |
Female | 27 | 27.0 | |
Total | 100 | 100.0 | |
3 | |||
Less than 30 years | 32 | 32.0 | |
41–50 years | 54 | 54.0 | |
51 years and above | 14 | 14.0 | |
Total | 100 | 100.0 | |
4 | |||
Near | 66 | 68.0 | |
Far | 31 | 32.0 | |
Total | 97 | 100.0 |
6.2. Bushmeat extraction activities/methods in the different land-use within the study area
A total of 26 (25.5%) wire snares, 20 (19.5%) spent cartridges, 7 (6.9%) hunters encountered, 33 (32.4%) gunshots, 3 (2.9%) hunters’ camps, and 13 (12.8%) were recorded for a total of 64 km of transects walked (Table 2). The most pronounced of all the bushmeat extraction activities was the use of guns (32.4%). The next being wire snares (19.5%). Most of the hunters set their wire snares in the rainy season. This is due to poor and very little visibility. Traps were monitored and checked between 2 and 3 days by those who set them, who were indigenes of the selected support zone communities around Cross River National Park villages. The rationale behind checking traps between 2 and 3 days was to reduce the time being invested into the traps checking, especially when quite a number of traps are set. Trap/wire snare setting is rampant during the rainy season. This is because there is less time to consummate hunting expedition. The equipment currently used by communal hunters is unsuitable for rational utilization of wildlife because it does not permit selective hunting. Communal hunters sell part of their bag at moderate prices to intermediaries who in turn supply markets, restaurants, and consumers in both rural and urban areas [33].
Bush-meat extraction activities/methods | Land-use | |||||
---|---|---|---|---|---|---|
Close canopy | Secondary forest | Farm fallow | Plantation | Total | Percentage | |
Wire snare | 9 | 1 | 15 | 1 | 26 | 25.5 |
Spent cartridges | 9 | 4 | 7 | 0 | 20 | 19.5 |
Hunters encounter rate | 2 | 0 | 5 | 0 | 7 | 6.9 |
Gunshots heard/guns | 15 | 3 | 15 | 0 | 33 | 32.4 |
Number of hunters camp | 3 | 0 | 0 | 0 | 3 | 2.9 |
Number of hunting trails | 10 | 3 | 0 | 0 | 13 | 12.8 |
6.3. The rate of utilization and consumption of bushmeat within the study area
Table 3 shows that 86% (
S/N | Variable | Frequency | % |
---|---|---|---|
1 | |||
Yes | 86 | 86.0 | |
No | 14 | 14.0 | |
2 | |||
Direct hunting | 8 | 13.3 | |
Indirect hunting | 18 | 30.0 | |
Buying | 33 | 55.0 | |
Gift | 1 | 1.7 | |
3 | |||
Weekly | 27 | 27.8 | |
Fortnight | 4 | 4.1 | |
Monthly | 19 | 19.6 | |
Occasionally | 37 | 38.1 | |
Never | 10 | 10.3 | |
Figure 2a shows that 88% (
6.4. Perceptions of communities’ members on status of wildlife and establishment of community-based wildlife management (CBWM)
Table 4 shows the relationship between the communities’ members’ perception on status of wildlife resources in the study area and the establishment of community-based wildlife management program in the area. The result shows that both variables are significant at 0.05 levels (2-tailed). The communities’ members are aware of the dwindling population status of wildlife resources in the study area. This therefore means that for the status of wildlife to stabilize and improve, there is need to have the establishment of community-based management of wildlife resources. According to Roe [46], community wildlife management is a strategy that is based on the assumption that it is possible to improve rural livelihoods, conserve the environment, and promote economic growth. Thus, effective wildlife management models need to be developed to secure bushmeat as resource and make it available for future generations. While wildlife resources in some countries in Africa is communally owned, in most countries, wildlife is a state property and hunting is often illegal, leading to a situation of low ownership and nonrecognition of user rights by the communities and even criminalization of use in the extreme cases. In order to address this situation, many countries are seeking ways to devolve and cede user rights to communities to create an incentive to invest in the long-term sustainable use of resources [47] in the form of community wildlife management arrangement.
Perception of communities' members | ||
---|---|---|
Perception of communities' members | Pearson correlation | 1 |
70 | ||
Wildlife status in the study area | Wildlife status in the study area Pearson correlation | 0.760 |
Sig. (2-tailed) | 0.021* | |
38 | ||
Establishment of CBWM program | Establishment of CBWM program Pearson correlation | 0.864 |
Sig. (2-tailed) | 0.013* | |
67 |
7. Conclusion
Given the different positions on bushmeat extraction activities/methods, rate of utilization/consumption of bushmeat, indiscriminate killing of bushmeat, and perception of communities’ members on establishment of community-based wildlife management, the study indicated high level of hunting activities resulting from the use of unsustainable hunting methods, high demand for bushmeat, and lack of capacity to control hunting in the park. Large mammals are especially exposed and become easy targets for hunters. Changes in traditional hunting practices through the use of improved hunting technology have decreased the likelihood that hunting will be sustainable. Therefore, protecting wildlife through protected area systems and development of biodiversity and corridors is the method which has the greatest potential to address global concerns regarding wildlife populations in the Oban Sector of Cross River National Park and West Africa at large. Alternatively, sport hunting and ecological tourism could serve as potent weapon in arresting the downward slide of wildlife resources in the park. To be truly effective, these kinds of efforts would have to be done in full collaboration with local communities, addressing issues of access and user rights, enforcement concerns, and lack of adequate data on population dynamics. Finally, to achieve the levels of protection necessary, habitat preservation therefore remains the key criterion for any conservation program, for without sufficient quantity and quality of habitat there will be no viable wildlife population to protect.
Acknowledgments
We are grateful to the Volkswagen Foundation, Hanover, Germany, for providing the grant to the University of Ibadan, Nigeria, within its ‘Africa Initiative’- ‘Knowledge for Tomorrow Cooperative Research Projects in Sub-Saharan Africa’ which made this study possible. We thank Federal Board for National Park Service, Abuja, the Conservator of Cross River National Park and other members of staff of the Cross River National Park, for their kind assistance in planning and logistics.
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