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Original Article
Perception and Attitude of People towards Wildlife in Communities around Kainji Lake National Park, Niger State, Nigeria: Implication on Biodiversity Conservation
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Bunza M. S. 1*, Abosede O. Omonona 2, Dododawa Z. 3 1 Department of Forestry and
Environment, Usmanu Danfodiyo
University Sokoto, Nigeria 2 Department of Wildlife and Ecotourism
Management, University of Ibadan, Nigeria 3 Department of Forest Resources and Wildlife
Management, University of Benin, Nigeria |
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ABSTRACT |
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Protected areas (PA) provide valuable habitats for wildlife and are considered as ecotourism hotspots, worldwide. Nonetheless, wild animals can have significant impacts on livelihoods of communities surrounding PA. In turn, locals can develop a negative attitude towards wildlife, escalating conflict and undermining conservation initiatives. However, there is paucity of information on factors influencing peoples' perception and attitude towards wildlife in Kainji Lake National Park (KLNP). Therefore, this study was designed to examine the factors influencing perception and attitude of people towards wildlife in KLNP. Communities were stratified into three groups: A (<3 km), B (3-6 km) and C (>6 km), based on their distances from KLNP boundary. Twenty three communities were purposively selected based on accessibility. A total of three hundred and twenty two (322) household heads were conveniently selected for this study. Data were analyzed using descriptive statistics and logistic regression at α0.05. Majority (66.1%) of the respondents are male, married (78.3%), and they are mostly farmers (52.8%) with an annual income ranging from ₦100,000-₦200,000.00. Significant positive predictors of household attitude towards wild animals were income (β=2.14) and education (β=1.01) in communities A (R2=0.41). Gender (β=0.63) and crop raiding (β=-2.15) were significant positive and negative predictors of respondents’ attitude in communities B (R2=0.23). Only destruction of stored food (β =0.171) was a significant positive predictor of households’ attitude in communities under category C (R2=0.36). Income (β=1.527) and education (β=1.228) were significant positive predictors of perception in category A while income (β=2.446) and education (β=0.942) predicted respondents’ perception in communities under category C (R2=0.17). Expansion of formal and adult education as well as livelihood diversification (skills acquisition programs) would go a long way in improving community attitude towards wildlife. Keywords: Attitude, Households, Crop raiding,
Wildlife Conservation |
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INTRODUCTION
Generally
speaking, rural communities in developing countries have little concern for
game species and see them exclusively in terms of their meat value and a threat
to their survival. This ugly perception is more common in adjoining communities
of protected areas where peoples’ interaction with wild animals imposed daily
costs on rural areas Anthony et al. (2010). In turn, locals can develop a negative
attitude towards wildlife, escalating conflict and undermining conservation
initiatives. The longstanding negative attitude of local people towards game
species originates from losses (human life, properties, field crops and even
cultivated lands used for conservation purposes) encountered during the
interface. Nowadays, linking of wild animals with conflict is now well
ingrained in the psyche of rural residents to the extent they can even blame
innocent and beneficial species Andrade and Rhodes (2012). The tolerance level for conflicts by rural
communities depends on the nature of the damage or species involved in the
conflict Browne-Nuñez and Jonker (2008). For instance, local communities in Africa
generally have a complex and negative perception towards lions, elephant and
crocodiles Carter et al. (2013). And there appears to be very little native
knowledge left regarding the functions of these species in the natural
ecosystems, particularly crocodiles Dickman (2010)
Over the past few
years, wildlife and human competition for resources and space has escalated due to the alteration of natural environments
from primarily wild to modified landscapes. As a result of the swift expansion
of human populations, and the rapid growth of settlements, competition for
resources has even reached unprecedented levels Food and Agriculture Organization (2009). Wildlife habitats have drastically
decreased as a result of the conversion of forested areas into other uses, such
as agriculture and human settlements, brought on by the growing demand for
land, energy, and raw materials. Animal populations were pushed into smaller
areas as a result of the destruction, fragmentation, and isolation of natural
habitats, which also increased the level of conflict between humans and
wildlife. These increases more chances of conflict as wildlife tend to meet
their needs in terms of nutrition, ecology, and behavior
Mc Guinness and Taylor (2014), Idowu et al. (2011), Milupi et al. (2023). Despite the fact that almost all nations
are affected by Human-Wildlife Conflict, some countries (developing nations)
such as Tanzania, Ethiopia, Kenya and Nigeria are at higher risk than developed
countries like UK and USA since agriculture and livestock are essential
component of rural livelihoods in these areas Kideghesho et al. (2007), Lamarque et al. (2009).
Managing
Human-Wildlife Conflicts requires not only a scientific understanding of the
issues but also an evaluation of the local population's attitudes toward
wildlife McGregor (2004). According to Odebiyi and Alarape (2017), in order to make sure that biodiversity
conservation policies are successful and appropriate for the local environment,
it is critical to understand social factors, such as the attitudes of the local
population, which provide a broad picture of the cultural, social and political
background of human-wildlife conflict. Evaluating the attitudes of the local
population can reveal information about their future behavior
that include but not limited to their readiness to coexist with wild animals,
compliance with the rules governing the use of the park resources, their
responses to financial losses brought on by wildlife and so on
By conducting
surveys to gauge public opinion, it is possible to forecast how public opinion
will affect conservation policies and vice versa, enabling a robust planning
and management techniques Omonona et al. (2017), Shibia (2010). Attitudes of the local population toward
conservation were adversely affected by the potential threat of conflicts
between people and wild animal species. Locals' attitudes toward wildlife are
also influenced by their personal experiences and beliefs, as well as the
various economic, legal, social, and ecological considerations Tarrant et al. (2016), Tessema et al. (2010). Effective conservation measures are
unlikely to be successful without comprehensive knowledge about the conflict
and the attitudes of the local population toward wildlife.
Materials and Methods
Description of the study area
The Kainji Lake
National Park (KLN) covers an area of over 2000 square miles (over 5000 square kilometer), straddling two Nigerian states (Kwara and
Niger). The park was legally created in 1979 via decree 46 of 1979 by the
amalgamation of two former game reserves (Borgu and Zugurma).
It’s Nigeria’s first ever national park. Historically, the park is a home to
several plants and animal species, including hydrological, cultural and human
resources. The common tree species in and around the park include Burkea Africana, Deterium macrocarpum, Afzelia Africana, Isoberlina tementosa and Acacia
species Umuziranenge (2019). The park falls under the northern guinea
savanna. The common fauna species in the
park include Buffalo (Syncerus cafer), Buffon’s Kob
(Kobus kob kob), Olive
baboon (Papio anubis), Roan antelope (Hippotragus equinius), African Bush Elephant (Loxodonta africana), Senegal kob (Kobus kob), Western hartebeest (Alcelaphus
buselaphus), Bush buck (Tragelaphus scriptus),
Hippopotamus (Hippopotamus amphibus), among others Zaffar et al. (2015). Every year, August and September see the
most rainfall, with totals ranging from 975 to 1220 mm. The months of March and
April typically see the highest temperatures (up to 380C). Although the park is
only 500 km away from Abuja, getting there takes eight to ten hours because of
the bad state of the roads.
Data collection
Data collection is
principal to a research activity particularly a research
that include qualitative approach. Therefore, considering the nature of this
research, questionnaire administration and Focus Group Discussion (FGD) were
used in this study. Semi-structured questionnaire was used to elicit
information on peoples’ perception and attitude towards wildlife. The
questionnaires were mainly targeted on households’ heads in the selected
communities. But in case of the absence of household head, the most elderly
member of the respective household was considered to participate in the study.
Questionnaires were administered face to face at the residents’
of the participants by the researcher and two other field assistants. Field
assistants were trained by the researcher before the commencement of the study.
Information on the list of communities and the number of households in each
community was obtained from the existing record of the park and traditional
rulers of the respective communities.
The relevance of
FGD is to obtain additional information to the one provided by the
questionnaire. In other words, FGD can help to obtain information that the
questionnaire may not be able to capture. Data were gathered and incorporated
in the results and discussion in a narrative form, following (20). Three (3)
focus group discussions (FGD) involving 12 individuals per groups were
considered for this study. Three age groups were formed and considered for FGD.
The first group comprised of elderly male participants (50-60 years), second
group consists of adult male of middle age (25-35 years) and the third group
comprised of elderly female individuals (50-60 years). Meanwhile, all the
necessary persons and facilities needed for the successful conduct of this work
were made available prior to the commencement of the study.
Sampling procedure and sample size
This study
employed a multi-stage sampling technique. In the first stage, all the
communities adjacent to Kainji Lake National Park were stratified by distance into
three groups: A (<3 km), B (3-6 km) and C (>6 km). In the second stage,
among the communities in the three strata, twenty-three (23) out of thirty-six
(36) communities were purposively selected at 30% intensity, proportionate to
size (322). Three hundred and twenty-two (322) copies of questionnaire were
administered to the sampled households Table 1 to get information on the perception and
attitude of households towards wildlife, as well as management strategies
adopted. This is in line with the method used by (21).
Table 1
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Table 1 Sample Size Distribution |
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|
S/N |
Sector |
Communities |
Sample frame |
Sample size (30%) |
Sub-Total |
|
|
|
Category A (>3km) |
|
|
|
|
1 |
Zugurma |
Fallagi |
40 |
12 |
|
|
2 |
|
Patiko |
25 |
8 |
|
|
3 |
|
Ibbi |
160 |
48 |
|
|
4 |
|
Mule |
15 |
5 |
108 |
|
5 |
|
Wuromakoto |
35 |
11 |
|
|
6 |
Borgu |
Malale |
60 |
18 |
|
|
7 |
|
Tungar Magawata |
20 |
6 |
|
|
|
|
Category B (3-6km) |
|
|
|
|
8 |
|
Poto |
20 |
6 |
|
|
9 |
Zugurma |
Tungar maje |
50 |
15 |
|
|
10 |
|
Tungar taya |
30 |
9 |
|
|
11 |
Borgu |
Woro |
40 |
12 |
|
|
12 |
|
Nukku |
45 |
14 |
106 |
|
13 |
|
Tungar mabudi |
55 |
17 |
|
|
14 |
|
Lumma sanke |
80 |
24 |
|
|
15 |
|
Tungar Bala |
30 |
9 |
|
|
|
|
Category C (>6km) |
|
|
|
|
16 |
|
Mazakuka |
25 |
8 |
|
|
17 |
Zugurma |
Shafini |
40 |
12 |
|
|
18 |
|
Sabon-pegi |
25 |
8 |
|
|
19 |
|
Gwaji |
15 |
5 |
|
|
20 |
|
Ibrahim lete |
20 |
6 |
108 |
|
21 |
Borgu |
Kilolio |
30 |
9 |
|
|
22 |
|
Leshibge |
20 |
6 |
|
|
23 |
|
Wawa |
180 |
54 |
|
|
|
|
Total |
1,060 |
322 |
322 |
Results and Discussion
Socioeconomic Factors of Households in the Sampled Communities around Kainji Lake National Park (KLNP)
Results displayed
in Table 2, revealed that most of the households
participated in this study were males (66.1%), who were between the ages of 41
and 50 (36.3%), followed keenly by the 30-40 years group with 30.4% while above
60 years group had the lowest representation, Majority (78.3%) are married
while the least (5.3%) of the respondents are singles. Majority had a household
size of 6-10 members. Many (33.2%) had an average annual income of
₦100,000.00 to ₦200, 0000.00, who are mostly farmers (58.2%).
Table 2
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Table 2 Socioeconomic Characteristics of Sampled
Households in Communities around Kainji Lake National Park |
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|
Variables |
Percentage (%) |
|
|
Gender |
|
|
|
Male |
213 |
66.1 |
|
Female |
109 |
33.9 |
|
Age |
|
|
|
20-30years |
17 |
5.3 |
|
31-40years |
98 |
30.4 |
|
41-50years |
117 |
36.3 |
|
51-60years |
62 |
19.3 |
|
Above
60years |
28 |
8.7 |
|
Marital
status |
|
|
|
Married |
252 |
78.3 |
|
Single |
17 |
5.3 |
|
Widow |
35 |
10.9 |
|
Divorcee |
18 |
5.6 |
|
Educational
status |
|
|
|
None |
87 |
27 |
|
Primary |
95 |
29.5 |
|
Secondary |
82 |
25.5 |
|
College |
20 |
6.2 |
|
Polytechnic |
24 |
7.5 |
|
University |
14 |
4.3 |
|
Household
Size |
|
|
|
01-May |
102 |
31.7 |
|
06-Oct |
70 |
21.7 |
|
Nov-15 |
120 |
37.3 |
|
Above
15 |
30 |
9.3 |
|
Occupation |
|
|
|
Farmer |
170 |
52.8 |
|
Civil
servant |
63 |
19.6 |
|
Business |
89 |
27.6 |
|
Annual
Income |
|
|
|
<
₦100,000.00 |
30 |
9.3 |
|
₦100,000-200,000.00 |
117 |
36.4 |
|
₦201,000-300,000.00 |
78 |
24.2 |
|
>
₦300,000.00 |
97 |
30.1 |
|
Source: Field survey (2021) |
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Table 3
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Table 3 Distribution of Respondents’ Attitude
Towards Wildlife Conservation in the Study Area |
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|
Attitudinal statements SA |
A |
|
N |
D |
SD |
Mean |
Standard Deviation |
Ranking |
|
|
Human-Wildlife Conflict should best be
addressed by all stakeholders |
25 (7.8) |
55 (17.1) |
12 (3.7) |
104 (32.3) |
126 (39.1) |
4.1366 |
1.14656 |
1st |
|
|
I believed in reporting conflict to
the appropriate authorities |
20 (6.2) |
51 (15.8) |
36 (11.2) |
142 (14.1) |
73 (22.7) |
4.0807 |
1.13002 |
2nd |
|
|
Human-Wildlife Conflict should best be addressed by park staff and
community leaders only |
11 (3.4) |
53 (16.6) |
29 (9.0) |
110 (34.2) |
119 (37.0) |
3.7826 |
1.23397 |
3rd |
|
|
Compensation due to wildlife attack
and crop raiding is adequate |
33 (10.2) |
64 (19.9) |
30 (9.3) |
112 (34.8) |
83 (25.8) |
3.0186 |
1.62715 |
4th |
|
|
Human-Wildlife Conflict should best be
addressed by park staff only |
150 (46.6) |
101 (31.4) |
34 (10.6) |
21 (6.5) |
16 (5.0) |
2.9658 |
1.46041 |
5th |
|
|
Management response to reported cases
of conflicts has increase Human-Wildlife Conflict in the study area |
41 (12.7) |
63 (19.6) |
41 (12.7) |
106 (32.9) |
71 (22.0) |
2.6801 |
1.34888 |
6th |
|
|
Traps that injured or kill wild animals
should be used by farmers |
36 (11.2) |
89 (27.6) |
63 (19.6) |
92 (28.6) |
41 (12.7) |
2.5404 |
1.33486 |
7th |
|
|
Wild animals involved in the
conflicts should be remove completely from the park |
164 (50.9) |
93 (28.9) |
27 (8.4) |
21 (6.5) |
17 (5.3) |
2.3882 |
1.17671 |
8th |
|
|
The best way to deal with wild animals
involved in the conflicts is to kill them |
108 (33.5) |
123 (38.2) |
26 (8.1) |
43 (13.4) |
22 (6.8) |
2.2205 |
1.32945 |
9th |
|
|
I support the use of poison to wild
animals from attack and destroying my crops |
64 (19.9) |
74 (23.0) |
42 (13.0) |
71 (22.0) |
71 (22.0) |
2.1522 |
1.18603 |
10th |
|
Results on peoples’ perception towards Wildlife in communities around Kainji Lake National Park, Nigeria
Results presented
in Table 3 and Table 4 indicated that the residents have a positive
attitude towards the attitudinal and perception statements towards wildlife
conservation in KLNP.
Table 4
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Table 4 Distribution of Respondents’ Perception
Towards Wildlife Conservation in the Study Area |
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|
Perception
statements |
SA |
A |
N |
D |
SD |
Mean |
Standard
Deviation |
Ranking |
|
The rate of Human-Wildlife Conflict
has increased in this area |
36 (11.2) |
60 (18.6) |
73 (22.7) |
98 (30.4) |
55 (17.1) |
2.7640 |
1.25311 |
13th |
|
Conservation
of wild animals in this area should continue |
121 (37.6) |
91 (28.3) |
28 (8.7) |
48 (14.9) |
34 (10.6) |
3.6739 |
1.38163 |
4th |
|
Wild animals living around this
household has increased |
51 (15.8) |
61 (18.9) |
84 (26.1) |
93 (28.9) |
33 (10.2) |
3.0714 |
1.23470 |
8th |
|
Proximity
to the park is the major factor to Human-Wildlife Conflict in this area |
51 (15.8) |
61 (18.9) |
84 (26.1) |
93 (28.9) |
33 (10.2) |
3.0124 |
1.23545 |
9th |
|
Vegetation structure around farmlands increase the rate of
Human-Wildlife Conflict in this area |
102 (31.7) |
78 (24.2) |
58 (18.0) |
47 (14.6) |
37 (11.5) |
3.5000 |
1.36774 |
5th |
|
Wild animal
species are serious threat to the safety and food security of the members of
this household |
122 (37.9) |
94 (29.2) |
32 (9.9) |
51 (15.8) |
23 (7.1) |
3.7484 |
1.30255 |
3rd |
|
Human-Wildlife Conflict around the
park is being exaggerated |
70 (21.7) |
57 (17.7) |
62 (19.3) |
70 (21.7) |
63 (19.6) |
3.0031 |
1.43281 |
10th |
|
Human-Wildlife
Conflict is a serious threat to wildlife conservation |
73 (22.7) |
75 (23.3) |
67 (20.8) |
93 (28.9) |
14 (4.3) |
3.3106 |
1.22912 |
7th |
|
Human-Wildlife Conflict a serious
threat to community livelihood |
85 (26.4) |
75 (23.3) |
64 (19.9) |
77 (23.9) |
21 (6.5) |
3.3913 |
1.28094 |
6th |
|
I am
ready to put my best to ensure that
Human-Wildlife Conflict is prevented/control in this area |
133 (41.3) |
94 (29.2) |
54 (16.8) |
28 (8.7) |
13 (4.0) |
3.9503 |
1.13731 |
1st |
|
I really care about the success of
this park |
119 (37.0) |
116 (36.0) |
33 (10.2) |
40 (12.4) |
14 (4.3) |
3.8882 |
1.16273 |
2nd |
|
Wildlife
resources in the National Park are the gift of nature and should be use
anyhow |
26 (8.1) |
93 (28.9) |
58 (18.0) |
142 (44.1) |
3 (0.9) |
2.9907 |
1.04564 |
11th |
|
Pastoralist are more affected by Human-Wildlife Conflict than surrounding
communities |
48 (14.9) |
17 (5.3) |
47 (14.6) |
197 (61.2) |
13 (4.0) |
2.6584 |
1.14443 |
14th |
|
The rate of
employment in this community has increased due to the National Park |
49 (15.2) |
29 (9.0) |
96 (29.8) |
138 (42.9) |
10 (3.1) |
2.9037 |
1.11631 |
12th |
|
The rate of Human-Wildlife Conflict
has increased in this area |
36 (11.2) |
60 (18.6) |
73 (22.7) |
98 (30.4) |
55 (17.1) |
2.7640 |
1.25311 |
13th |
|
Conservation
of wild animals in this area should continue |
121 (37.6) |
91 (28.3) |
28 (8.7) |
48 (14.9) |
34 (10.6) |
3.6739 |
1.38163 |
4th |
|
Wild animals living around this
household has increased |
51 (15.8) |
61 (18.9) |
84 (26.1) |
93 (28.9) |
33 (10.2) |
3.0714 |
1.23470 |
8th |
|
Proximity
to the park is the major factor to Human-Wildlife Conflict in this area |
51 (15.8) |
61 (18.9) |
84 (26.1) |
93 (28.9) |
33 (10.2) |
3.0124 |
1.23545 |
9th |
|
Vegetation structure around farmlands increase the rate of
Human-Wildlife Conflict in this area |
102 (31.7) |
78 (24.2) |
58 (18.0) |
47 (14.6) |
37 (11.5) |
3.5000 |
1.36774 |
5th |
|
Wild animal
species are serious threat to the safety and food security of the members of
this household |
122 (37.9) |
94 (29.2) |
32 (9.9) |
51 (15.8) |
23 (7.1) |
3.7484 |
1.30255 |
3rd |
|
Human-Wildlife Conflict around the
park is being exaggerated |
70 (21.7) |
57 (17.7) |
62 (19.3) |
70 (21.7) |
63 (19.6) |
3.0031 |
1.43281 |
10th |
|
Human-Wildlife
Conflict is a serious threat to wildlife conservation |
73 (22.7) |
75 (23.3) |
67 (20.8) |
93 (28.9) |
14 (4.3) |
3.3106 |
1.22912 |
7th |
|
Human-Wildlife Conflict a serious
threat to community livelihood |
85 (26.4) |
75 (23.3) |
64 (19.9) |
77 (23.9) |
21 (6.5) |
3.3913 |
1.28094 |
6th |
|
I am
ready to put my best to ensure that
Human-Wildlife Conflict is prevented/control in this area |
133 (41.3) |
94 (29.2) |
54 (16.8) |
28 (8.7) |
13 (4.0) |
3.9503 |
1.13731 |
1st |
|
I really care about the success of
this park |
119 (37.0) |
116 (36.0) |
33 (10.2) |
40 (12.4) |
14 (4.3) |
3.8882 |
1.16273 |
2nd |
|
Wildlife
resources in the National Park are the gift of nature and should be use
anyhow |
26 (8.1) |
93 (28.9) |
58 (18.0) |
142 (44.1) |
3 (0.9) |
2.9907 |
1.04564 |
11th |
|
Pastoralist are more affected by Human-Wildlife Conflict than surrounding
communities |
48 (14.9) |
17 (5.3) |
47 (14.6) |
197 (61.2) |
13 (4.0) |
2.6584 |
1.14443 |
14th |
|
The rate of
employment in this community has increased due to the National Park |
49 (15.2) |
29 (9.0) |
96 (29.8) |
138 (42.9) |
10 (3.1) |
2.9037 |
1.11631 |
12th |
Factors influencing perception of the sampled households towards wildlife in KLNP
Table 5 displays the results on how the different
forms of conflict and some socioeconomic parameters of the sampled households
were used to predict people’s perception of wildlife in KLNP. This further
reveals that income (ß=1.527), education (ß=1.228) and Crop raiding (ß=-1.573)
influenced the perception of the sampled households in category A.
Additionally, income (ß=2.446), education (ß=0.942) and crop raiding (ß=-1.634)
influenced households’ attitude in category B while income (ß=1.767) and crop
raiding (ß=-1.247) were found to be significant positive and negative
predictors of households’ attitude in communities under category C.
Table 5
|
Table 5 Factors Influencing Perception of
Households Among the Three Categories of Communities (A, B and C) Towards
Wildlife Conservation in Kainji Lake National Park (N=322) |
||||
|
Communities |
Variables |
Coefficient values (ß) |
Std. error |
α0.05 |
|
Category A (<3km) |
Perception |
|
|
|
|
|
Income |
1.527 |
0.283 |
0.004 |
|
|
Household size |
0.339 |
0.134 |
0.521 |
|
|
Education |
1.228 |
0.144 |
0.000 |
|
|
Gender |
-0.594 |
0.223 |
0.519 |
|
|
Marital status |
-0.101 |
0.155 |
0.214 |
|
|
Crop raiding |
-1.573 |
0.637 |
0.008 |
|
|
Livestock depredation |
-1.750 |
0.162 |
0.001 |
|
|
Human attack |
1.063 |
0.418 |
0.265 |
|
|
Destruction of stored foods |
-0.173 |
0.153 |
0.082 |
|
Category B (3-6km) |
Perception |
|
|
|
|
|
Income |
2.446 |
0.236 |
0.000 |
|
|
Household size |
-0.552 |
0.731 |
0.265 |
|
|
Education |
0.942 |
0.261 |
0.002 |
|
|
Gender |
0.753 |
0.143 |
0.063 |
|
|
Marital status |
1.212 |
0.318 |
0.065 |
|
|
Crop raiding |
-1.634 |
0.236 |
0.001 |
|
|
Livestock depredation |
0.699 |
0.321 |
0.081 |
|
|
Human attack |
0.519 |
0.274 |
0.461 |
|
|
Destruction of stored foods |
0.532 |
0.461 |
0.436 |
|
Category C (>6km) |
Perception |
|
|
|
|
|
Income |
1.767 |
0.425 |
0.002 |
|
|
Household size |
0.398 |
0.527 |
0.363 |
|
|
Education |
-1.637 |
0.218 |
0.631 |
|
|
Gender |
0.682 |
0.431 |
0.241 |
|
|
Marital status |
0.813 |
0.241 |
0.674 |
|
|
Crop raiding |
-1.247 |
0.683 |
0.004 |
|
|
Livestock depredation |
0.635 |
0.442 |
0.522 |
|
|
Human attack |
1.433 |
0.251 |
0.469 |
|
|
Destruction of stored foods |
0.073 |
0.826 |
0.087 |
|
Category A (R2=0.37), Category B (R2=0.29) and
Category C (R2=0.17) |
||||
Table 6
|
Table 6 Factors Influencing the Attitude of
Households Among the three Categories (A, B and C) Towards Wildlife
Conservation in the Study Area |
||||
|
Communities |
Variables |
Coefficient values (ß) |
Std. error |
α0.05 |
|
Category A (<3km) |
Attitude |
|
|
|
|
|
Income |
2.141 |
0.462 |
0.000 |
|
|
Household size |
-1.725 |
0.612 |
0.071 |
|
|
Education |
1.014 |
0.381 |
0.002 |
|
|
Gender |
-0.684 |
0.871 |
0.082 |
|
|
Marital status |
-0.759 |
0.526 |
0.062 |
|
|
Crop raiding |
-0.915 |
0.383 |
0.001 |
|
|
Livestock depredation |
-1.186 |
0.841 |
0.003 |
|
|
Human attack |
-0.871 |
0.491 |
0.065 |
|
|
Destruction of stored foods |
-1.652 |
0.739 |
0.701 |
|
Category B (3-6km) |
Attitude |
|
|
|
|
|
Income |
-2.133 |
0.396 |
0.003 |
|
|
Household size |
-1.627 |
0.285 |
0.074 |
|
|
Education |
1.391 |
0.864 |
0.061 |
|
|
Gender |
0.631 |
0.423 |
0.000 |
|
|
Marital status |
1.897 |
0.372 |
0.073 |
|
|
Crop raiding |
-2.146 |
0.651 |
0.002 |
|
|
Livestock depredation |
0.731 |
0.910 |
0.060 |
|
|
Human attack |
1.643 |
0.527 |
0.921 |
|
|
Destruction of stored foods |
1.290 |
0.284 |
0.731 |
|
Category C (>6km) |
Attitude |
|
|
|
|
|
Income |
1.438 |
0.742 |
0.831 |
|
|
Household size |
0.647 |
0.352 |
0.641 |
|
|
Education |
0.924 |
0.547 |
0.523 |
|
|
Gender |
0.482 |
0.296 |
0.362 |
|
|
Marital status |
|
|
|
|
|
Crop raiding |
1.432 |
0.367 |
0.821 |
|
|
Livestock depredation |
0.779 |
0.584 |
0.094 |
|
|
Human attack |
0.534 |
0.718 |
0.231 |
|
|
Destruction of stored foods |
-0.171 |
0.631 |
0.004 |
|
Category A (R2=0.41), Category B (R2=0.23) and Category C (R2=0.36) |
||||
Ordinal Regression Results on Factors influencing Attitude of the Sampled Households towards Wildlife in KLNP
Table 6 revealed how the different forms of conflict
and some socioeconomic parameters were used to predict local people’s attitude
towards conservation around KLNP. Negative values obtained and presented in Table 6 means that the likelihood of the dependent
variables (attitude) falling at a higher level
decreases as the values of the independent variables rise. This
further reveals that income (ß=2.141), livestock depredation (-1.186)
and Crop raiding (ß=-0.915) were important predictors of attitude of the
sampled households in category A. Gender (ß=0.631) and crop raiding (ß=-2.146)
influenced households’ attitude in category B. However, only the destruction of
stored foods (ß=-0.171) was found to be a significant predictor of human
attitude in communities under category C.
Discussion
Perception and Attitude of the Sampled Households towards Wildlife in Communities around Kainji Lake National Park, Nigeria
Human-wildlife
conflict is increasing across Africa and enlisting the support of local people
is critical to conflict mitigation and conservation efforts. Information from
attitude surveys can inform management and policy decisions particularly in
situations of human-wildlife conflict. In the context of wildlife management,
perception studies tend to focus on people’s concern about the hazards they
associated with wild animals (22). Humans often make their decisions about wild
animals based on such perceptions. People’s response to wildlife disturbance
such as Human-Wildlife Conflict (HWC) and their understanding of the
characteristics of the conflict forms the basic and essential foundation on
which individuals’ develop their perception and
attitude. Therefore, for any conservation effort to be successful, the
influence of different forms of HWC and socioeconomic factors on the peoples’
perception and attitude need to be investigated. Because a feeble tolerance for
wildlife damage and negative attitude towards National Parks (NPs) can crippled
conservation efforts. Despite the report of different forms of conflict
experienced by the locals around KLNP, results on the attitude and perception
statements revealed that the mean score for the continuous conservation of
wildlife resources in the area was high Table 5 and Table 6. In addition, the summary of the mean score
of the different perception and attitudinal statements indicated that
respondents had either a positive perception/attitude towards conservation of
wildlife resources in the park or they are neutral, irrespective of their
distance to the boundary of the park. Unfavorable
attitudes towards wildlife by the study respondents were very low. This is
contrary to (23) who found that communities that experience more losses from
wild animals are less likely to support conservation efforts in protected
areas.
However, the
discovery of the positive attitude towards conservation by communities around
the study area is not an isolated case. This is because, (24) reported that
despite the damage caused by Olive baboon on farmlands around KLNP, which
include destruction of farm produce as well as other conservation induced
costs, communities around KLNP had a positive view of the conservation in the
park. When the sampled HH were asked to respond to those statements that have
to do with the killing or poisoning of the culprit animals, a significant
number of them strongly disagree with the idea Table 5 and Table 6. This indicated the high level of tolerance
of wildlife activities by the locals around the park. The tolerance level
recorded in this study may be linked to the outcome of the various mitigation
measures adopted and the timely response to the reported cases of conflict by
the park officials. It’s a well-known fact that wildlife resources are
protected by both local and international laws, and as such, the culprits may
face the wrath of law if apprehended. Therefore, the decision by the locals to
live in harmony with wildlife in the study area can further be attributed to
their fear of being arrested and prosecuted as highlighted by the majority of
the group discussants. This was further reaffirmed by (25) who reported that
majority of communities around the KLNP are aware of the laws guiding the park.
Some interviewees reported that part of the reason why they do not want to kill
animals when sighted in their farms was that sometimes the park rangers traced
the sound of gun shorts and later apprehend the culprits. This was further
confirmed during field work.
The locals'
enthusiastic views about wildlife may further be linked to the perceived
economic benefits derived from the park. This was corroborated with the
information obtained during focus group discussion, where majority said they
have been compensated for the loss of crops and livestock. In a related
development, interaction with the park staff revealed that some staff
attributed the positivity of the surrounding communities towards wildlife
resources in the park to the tangible benefits derived from the park. This is
in consonance with researches conducted in other part
of the world. For example, (26) reported that despite HWC in Nepal’s Chitwan
National Park, the locals associated income earned from tourism as the likely
reason why they expressed a more favorable attitude
towards conservation of tigers in the park.
Based on the report by (27) the positive attitude of the local
communities around KLNP was attributed to the financial benefits they derived
from tourism and employment opportunities with protected areas. According to
(28), people are more likely to support the presence of conservation areas if
benefits gained from them off set the associated cost. However, (29) indicates
that locals' attitudes toward wildlife are shaped by personal experiences and
beliefs, alongside economic, legal, social, and ecological factors. This means
that for community-based conservation, understanding individual encounters,
economic impacts, cultural beliefs, and the environmental context is crucial to
foster positive attitudes and effective wildlife management practices.
Studies on
people’s perception and attitude make it easy to predict how certain factors
will influence perception and attitude of locals towards wildlife resources and
how conservation policies will influence people’s attitude and perception
towards effective management of wildlife resources in protected areas (30). In
the present study, crop raiding, livestock depredation, income and educational
status Table 5 and Table 6 were found to be significant predictors of
people’s perception and attitude towards wildlife (regardless of the distance
of the communities to the park boundary). The likely reason why livestock
depredation was found to be a significant negative factor in predicting
perception and attitude may not be unconnected with the respondents’ livestock
holdings, as those who owned more domestic animals will be more likely to
depend on income from livestock than those with few numbers of animals. And
they tend to perceived potential predators as a
serious threat to their survival. This is in consonance with (31) who
discovered that respondents with high economic holdings of economically
important livestock, perceived wild animals to be a greater threat to their
survival. And coincidently, most of the group discussants claimed to have
considerable number of livestock. Educational status of the sampled households
also influenced their perception and attitude towards wildlife conservation in
KLNP. Implying that expansion of formal and adult education as well as
livelihood diversification would go a long way in improving community attitude
towards wildlife. This further revealed that attitude of the locals towards
conservation is better developed on the basis of education, income and crop
raiding. However, this means that educating the local people around the study
site about the needs and benefits of conserving wildlife resources and
compensating them on the loss of crops and livestock will go a long way in
gaining their participation in conservation initiatives. The results of this study further revealed
that about 37% and 41% changes in the attitude of the sampled households (HH)
in communities under category A (0-3km) is jointly explained by income and
education. The results revealed that those variables are important factors
influencing perception and attitude of locals towards wildlife. The coefficient
for crop raiding shows that all things being equal, a one percent decrease in
crop raiding will influence their attitude positively irrespective of their
gender. This is contrary to (32) who reported that only the gender influenced
attitude of locals where women showed significantly more negative attitude
towards wildlife than men. This further reveals that
if the current level of wildlife damage to crops is allowed to continue, it can
forced the locals to have a negative attitude towards
wildlife. Despite the level of HWC around KLNP, locals still have positive
attitude towards wildlife Table 3 and Table 4. But during focus group discussion; many
discussants cried out that more emphasis is given to care about wildlife than
human welfare. Therefore, this kind of perception need to be considered by the
park officials, as it would help in building more trust and establish good
rapport between the park officials and local people living around the park.
Despite the fact that not all forms of conflicts and socioeconomic factors
influenced peoples’ perception and attitude negatively, it cannot be concluded
that they are not likely to influence their perception
Conclusion
Local people
develop positive or negative attitudes towards wildlife conservation in the
study area due to different factors. The key factors influencing people’s
perception and attitude were mostly the risk of wildlife damage particularly
crop raiding, livestock depredation, destruction of properties and
socioeconomic factors such as education and income. This further revealed that
perception and attitude of the locals towards wildlife conservation is better
developed on the basis of education, income and prevention of crop raiding and
livestock depredation. One conservation significance of this work is that
majority of the sampled households were aware of conservations laws and ready
to comply with the law that established the park. Also, Residents with formal
education developed more positive attitude towards wildlife than the less
educated people.
ACKNOWLEDGMENTS
None.
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