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Abstract

Background and Research Aims

Biodiversity loss is a recent global crisis largely due to intense anthropogenic pressures. A study was conducted in Wenchi highlands in the late 2020 and early 2021 to explore the major challenges and opportunities for biodiversity conservation.

Methods

Data were collected using semi–structured questionnaires, focus group discussions and direct observations from four relatively accessible highland villages. The questionnaires were administered to 395 randomly selected household farmers based on their accessibility, presence of natural forest remnants and proximity to an iconic Lake Wenchi.

Results

The types of natural resource utilizations (χ²=87.94, df=4, P < 0.05) and the attitudes of the local community varied among the respondents (χ²=110.92, df=2, P < 0.05). The majority of the respondents used the natural resources as sources of firewood (70.19%) and for cattle grazing (63.51%). Most of the community members (56.47%) had a positive attitude towards biodiversity conservation. Only 12.14% had no idea about biodiversity conservation. The study also identified land-use changes, exotic plantations, soil erosion, illegal land grabbing, and burning of ericaceous belts as the major conservation challenges in the area. The severity level of conservation threats also varied significantly (χ²=243.519, df=6, P < 0.05). Overgrazing, firewood collection and land-use changes were the most serious biodiversity challenges. A unique topographic beauty, rich floras and faunas, recent global and regional recognitions, positive outlooks of the local people, and ecotourism development projects in the area were the main possible conservation opportunities.

Conclusion

Anthropogenic activities severely threatened Wenchi montane forests and wildlife therein. Potential conservation opportunities in the area, however, opens up the door for future conservation actions.

Implications for conservation

Wenchi highlands face severe conservation threats and need urgent conservation priorities and actions.

Keywords

Conservation challenges conservation opportunities local people montane forest Wenchi highlands wildlife conservation

Introduction

Biodiversity loss is increasing at an alarming rate across the globe (Mamabolo et al. 2020). Many of the pristine environments are long gone through habitat degradation and fragmentation (Martin et al. 2012; Torre et al. 2014). Thus, mosaics of agricultural land interspersed with remnant forest patches are now the norm in many tropical countries (Garcia et al. 2009), and preventing further biodiversity loss is one of the most pressing challenges of mankind (Pozo et al. 2021). Habitat fragmentation attracted worldwide public concern because it modified most of the natural habitats through habitat isolation and reducing habitats, and led to the rapid loss of biodiversity (Mesquita & Passamani, 2012).

African biodiversity is largely concentrated in human-dominated landscapes (Tyrrell et al. 2020). Most of the natural habitats in the Ethiopian highlands have also a high level of mammal endemism though they are threatened by intense and irreversible anthropogenic impacts (Abune, 2000; Fekadu et al. 2015; Lavrenchenko & Bekele, 2017). These anthropogenic pressures either fragmented or destroyed numerous natural wildlife habitats and their biodiversity (Musyoki et al. 2012; Kasso & Bekele, 2014; Petros et al. 2016; Legese et al. 2019; Abrehe et al. 2020). Many of the endemic mammals of the country in particular are heavily threatened (Lavrenchenko & Bekele, 2017). Such problems are much higher in areas outside protected areas (PAs). Although there is a consensus that protected areas alone are insufficient for conservation, conservation activities in the continent are still only focused on these (Garcia et al. 2009; Debby & Dick, 2012; Tyrrell et al. 2020).

In recent days, conservation advocates such as Convention on Biological Diversity (CBD) are pressing hard for the recognition of conservation initiatives beyond PAs (CBD, 2018; Tyrrell et al. 2020; Alves-Pinto et al. 2021). This has led to a shift in conservation measures, and the provision of equal conservation weights for natural habitats outside protected areas (Caro, 2001, 2002; Debby & Dick, 2012). Such conservation approach gained a momentum as it recognizes farmers as stakeholders in conserving biodiversity and actively solicits them as partners (Garcia et al. 2009; Pozo et al. 2021).

Wenchi highlands are among the pristine environments that are facing stiff conservation threats, and require thorough assessments for biodiversity conservation challenges, opportunities and other related studies. The montane forests around Lake Wenchi offer a natural habitat to various birds and mammals (Shale et al. 2014). However, these highland environments faced severe environmental degradation that threatened the health and livelihoods of the nearby community (Shale et al. 2014). As a result, natural forests are fragmented into numerous patches, and most of the medium to large-bodied mammals are pushed out from the remaining forests. The survival of species in modified habitats depends on the species ability to use available fragmented landscape units (Martin et al. 2012).

The wildlife conservation of Ethiopia is facing an intricate and complex challenge that needs to be addressed (Abune, 2000). Filling conservation knowledge gaps and improving conservation predictions are persistent technical challenges in conservation sciences (Hoffmann, 2021). Thus, making conservation information publicly available is the first step to solve this problem. However, there is no scientifically documented information on the challenges for biodiversity conservation in Wenchi highlands. Assessing the existing conservation opportunities has also far-fetching significance for conservation measures. Therefore, this study was aimed to document major conservation challenges and opportunities for biodiversity preservation in Wenchi highlands.

Methods

Study area description

The study was conducted in Wenchi highlands, southwest Shewa Zone, Oromia region of Ethiopia. The area is located between Ambo and Waliso towns, 155 km away from the capital, Addis Ababa (Figure 1). It is positioned between 2,810 to 3,386 m asl altitudinal ranges. The area is characterized by highland sub-humid climate with an average annual rainfall of 1410 mm (Shale et al. 2014; Tufa et al. 2020). The area receives unimodal rainfall type with a longer rainy period from May to September. The peak rainfall occurs in July and August, while the cold–dry season occurs between October and January (Tufa et al. 2020). The temperature of the area varies between 14 to 26^oC during the day and falls below 10^oC at night (Degefu & Schargel, 2015). It also varies between 18^oC to 25^oC during the wet and dry seasons, respectively (Degefu et al. 2014).

Figure 1.

Map of the study area (Adopted from Tufa et al. 2022).

Lake Wenchi is among the few remaining fairly pristine high–mountain crater lakes in the central highlands (Degefu & Schagerl, 2015; Tufa et al. 2020). The area also owns the 15^th century Monastery, mineral waters and hot springs (Degefu et al. 2014; Shale et al. 2014). Lake Wenchi watersheds are characterized by a sub-afro alpine vegetation type. The area is one of the popular tourist attractions and interesting ecotourism destinations of the country. As a result, the government of Ethiopia has launched ecotourism development initiative at Lake Wenchi watershed in 2021 as part of Gebete Lehager projects. Albesa Forest is another natural forest patch located outside Wenchi Lake escarpment in Cabo Sansalati village.

The main livelihoods in the area are mixed agriculture – crop cultivation and livestock rearing, small and micro-enterprises, and ecotourism (Shale et al. 2014; Tufa et al. 2022). The average land holding size for a single household is 0.5 ha, and the major crops grown in the area are enset (Ensete ventricosum), barley (Hordeum vulgare), wheat (Triticum species), and potato (Solanum tuberosum) (Shale et al. 2014). Like other highland farmers of the country, Wenchi highlands are a highly populated areas in the district (District Land Administration Office, 2020 unpl.), and farming and harvesting is performed by traditional technologies.

Ethical statement

The study adhered to the legal requirements of Ethiopia, and permission to carry out the study was obtained from the Department of Zoological Sciences, Addis Ababa University. Informed consent has been obtained verbally from all individuals included in this study. The study participants were also guaranteed that their responses are confidential and only used for this study.

Data collection

Primary and secondary sources of data were used to collect information about biodiversity conservation challenges and opportunities in Wenchi highlands. Primary data were collected using semi–structured questionnaires, focus group discussions, and direct observations. Secondary sources of data included journal articles, websites, and reports.

Wenchi district contains a total of eight highland villages – Haro Wenchi, Shagag Gafare, Waldo Telfami, Damu Dagale, Azar Qeransa, Cabo Sansalati, Merega Abayi and Odo Fura. Of these, four highland villages: Haro Wenchi (856 households), Waldo Telfami (783), Azar Qeransa (860) and Cabo Sansalati (681) were considered for this study because they are relatively accessible, contain natural forest remnants, and neighboring to an iconic Lake Wenchi. Haro Wenchi is a classic highland ecosystem with the highest elevation at Mount Wenchi (3,386 m asl), and Wenchi crater lake.

Household samples were computed using the formula, $n = Z^{2} 2 P (1 - P) / d^{2}$ ; where $n$ is calculated sample size, $Z$ is critical value (1.96) at 95 % confidence level, $P$ is an expected proportion (50%) and $d$ is precision or margin of error which is fixed at 5% (Daniel, 1995). Thus, the questionnaires were administered to a total of 395 (335 male and 60 female) household heads that were randomly selected from the study villages. Moreover, the calculated sample size was proportionally assigned to each of the four villages using the formula, $nh = \frac{N (n)}{\sum N}$ (Pandey & Verma, 2008); where, $nh$ is the number of sample households to be selected from each village N is the total number of households in each village $n$ is the calculated as total sample size to be selected from all the study villages, and $\sum N$ is the sum total of households in the selected villages. Accordingly, 104, 103, 94 and 82 households were selected from Azar Qeransa, Haro Wenchi, Waldo Telfami and Cabo Sansalati villages, respectively. Each household was randomly selected from these villages by lottery method using the lists obtained from their administrations for data collection.

A semi–structured questionnaire was designed in the way that enables the collection of relevant information. Both open and closed ended questions were prepared in English and administered using the local language, Afan Oromo. Each interview was conducted by one of the researchers and his field assistant for approximately 30 min in the late 2020 and early 2021. The questionnaire was composed of three parts. In the first part, demographic profiles, such as age, number of family members and level of education of the respondents were collected. The second section gathered information on the kind of natural resource used from the forests, and the attitudes of the local community towards the conservation. In the last part, conservation threats, their severity levels, and other related questions were presented.

Focus group discussions were conducted with key informants (village administrators, agricultural extension workers and selected farmer representatives) in the study villages to strengthen the information gathered through questionnaires. In the study villages, from 5 to 10 individuals participated in FGD. In addition to the above informants, ecotourism guides also participated in Haro Wenchi FGD. Focus group discussions were led by the researcher, and informants were encouraged to share their ideas openly and freely. Participatory discussions were made based on the summary of the semi-structured questionnaire that was prepared and filled in the interviews. Discussions were made on the dynamics and importance of the forest remnants, why the local people rely on its natural resources, the knowledge and attitudes of the local community towards biodiversity conservation, the prevailing conservation challenges and possible conservation opportunities and measures.

Moreover, direct field observations were carried out in order to personally confirm and document the specified prevailing conservation threats and opportunities in interviews and FGD. The number of firewood exploiters were also recorded during the direct observations. Individuals that were directly engaged on firewood collection, heading to forest with firewood collecting instruments such as ropes and axes, and carrying firewood were considered as firewood exploiters.

Data analyses

Quantitative data obtained from semi–structured questionnaires were analyzed using appropriate statistical methods such as percentage, and Chi–square test. Chi–square (χ²) tests were used to verify the possible variations in the socio-economic profiles and the responses of the participants. All statistical data were analyzed using SPSS version 21 (SPSS, Inc. USA), and probability values were considered statistically significant when P–value is < 0.05. Qualitative data obtained through focus group discussions, interviews and observations were systematically summarized, and analyzed by narration and descriptions through content analysis method.

Results

Sociodemographic profiles

From the total of 395 respondents, 335 (84.8%) were males and 60 (15.2) females. Large number of the respondents (82.2%) were between 20 and 50 age ranges. Most of the respondents (47.8%) were not registered for formal education, while 36.9% attended primary education. Majority of the respondents (86.5%) had between 5 and 10 family sizes, while the remaining had above 3 family members. The respondents spent from 5 years to more than 50 years on farming. Most of the respondents (78.2%) had a farmland size below one to two hectares, while only 11% of them had more than three hectares (Table 1).

Table 1.

Socio-demographic profiles of the study participants.

Variables		No. of respondents	Percentage (%)
Sex	Male	335	84.8
Sex	Female	60	15.2
Age in years	20–30	103	26.07
	31–40	138	34.93
	41–50	84	21.26
	>50	70	17.72
Educational status	Illiterate	189	47.84
	Primary education	146	36.96
	Secondary education	23	15.18
Family size	<5	117	29.62
	5–10	225	56.96
	>10	53	13.41
Farming years	<10	49	12.4
	10–20	90	22.78
	>20	256	64.81
Farmland size	<1ha	215	54.43
	1–2ha	94	23.79
	2.1–3ha	57	14.43
	>3ha	29	7.34
Economic activity	Ecotourism	60	15.18
Economic activity	Mixed farming	335	84.82

Most (84.8%) of the respondents supported their livelihoods through mixed farming practices. Only 15.2% of the respondents in Haro Wenchi village generated additional income through ecotourism. There were significant differences in the perceptions of the local community towards biodiversity conservation with respect to their level of education (χ²=411.79; df=2, P < 0.05), economic activity (χ²=36.26; df=1; P < 0.05), farmland size (χ²=140.21; df=2, P < 0.05) and family size (χ²=88.43, df=2, P < 0.05). However, there were insignificant differences with respect to age (χ²=2.79, df=3, P > 0.05), sex (χ²=0.109; df=1, P > 0.05), and duration in the area (χ²=2.791; df=2, P > 0.05).

Responses on natural resource utilizations

Majority of the respondents in the study area used the natural forests as sources of firewood (70.19%) and for cattle grazing (63.51%). Almost all of the respondents obtained firewood either directly or indirectly from the montane forests. There was no respondent that obtained charcoal from the forest remnants. The local community also used forest products and thatch grass as raw materials for house and fence constructions. Local communities also obtained some food items (wild honey and wild edible fruits) and other benefits in the form of animal fodder, medicinal plants, hot spring for bathing and mineral water for drinking, traditional farm wood product tools and as a source of income by selling thatching grass and firewood (Table 2). Statistically, a significant difference was observed among the forms of natural resource utilizations by the respondents (χ²=87.94, df=4, P < 0.05).

Table 2.

Types of natural resource utilizations by the local people in Wenchi highlands.

Villages	No. of participants	Forms of natural resource exploitation (%)
Villages	No. of participants	Grazing area	Firewood	Construction materials	Food sources	Other benefits
Haro Wenchi	103	81.74	96.10	46.53	38.96	43.75
Waldo Telfami	106	74.17	71.88	24.38	23.51	21.62
Cabo Sansalati	82	65.72	52.26	41.45	35.55	12.14
Azar Qeransa	104	32.43	60.53	33.16	12.32	8.21
Total	395	65.71	70.19	36.38	27.58	21.43

Cattle, small ruminants (sheep and goat), and horses and/or donkey are the major types of livestock reared by the Wenchi highland community (Table 3). Sheep (7 per households on average) are the most produced livestock in the area followed by cattle (averagely, 5 per household). Majority of the respondents used the natural habitats more as grazing areas for their livestock during the wet seasons than the dry seasons (53.84%). About 38.11% of the respondents, however, use the forest habitats for livestock grazing throughout the year. There were also a small number of households (12.25%) that did not use the forest habitats as grazing areas. Statistically, a significant difference was observed in livestock grazing intensity of the natural habitats by the respondents (χ²=137.70, df=2, P < 0.05).

Table 3.

Type and number of livestock/households and grazing intensity on natural habitats.

Villages	N	Livestock/households			Grazing intensity
Villages	N	Cattle	Sheep	Horses/Donkey	Year round	Wet season	Never used
Haro Wenchi	103	5	8	2	46.24	53.86	12.80
Waldo Telfami	106	4	6	2	25.81	40.73	10.62
Cabo Sansalati	82	6	6	1	38.65	48.42	13.37
Azar Qeransa	104	5	10	2	41.74	54. 65	12.24
Average	395	5	7.5	1.75	38.11	50.32	12.25

Local community attitudes towards conservation

Majority of the respondents had positive attitudes (56.47%) and the least number (12.14%) had no idea towards conservation of biodiversity in Wenchi highlands (Table 4). A significant difference was observed among the attitudes of the given respondents (χ²=110.92, df=2, P < 0.05). Individuals that have a positive attitude considered the economical, ecological and aesthetic values of the natural environments, and most of them were from Haro Wenchi village.

Table 4.

Local community attitudes towards biodiversity conservation in Wenchi highlands.

Villages	No. of respondents	Local community attitudes (%)
Villages	No. of respondents	Positive	Negative	Neutral
HaroWenchi	103	71.55	26.47	15.72
Waldo Telfami	106	52.34	35.32	12.16
Cabo Sansalati	82	55.71	33.54	11.24
Azar Qeransa	104	46.28	30.41	9.43
Total	395	56.47	31.39	12.14

The local people also reflected on the existing conservation threats and their severity levels (Table 5). The majority of the respondents (40%) stated that Wenchi natural habitats and their biodiversity are highly threatened. About 27% of the respondents, however, rated the threats at a low level. There was a significant difference on the severity level of conservation threats (χ²=243.519, df=6, P < 0.05).

Table 5.

Biodiversity threats with their severity levels in Wenchi highlands (N= 395; HW = Haro Wenchi).

Threat type		Severity impact level (%)			No. of respondents	Areas of occurrences
Threat type		High	Medium	Low	No. of respondents	Areas of occurrences
Overgrazing		40.62	42.25	17.13	395	In all villages
Human settlement		45.34	33.14	20.52	395	In all villages
Farmland expansions		56.53	27.83	15.64	395	In all villages
Fuelwood collection		63.37	24.15	12.48	395	In all villages
Exotic plantations		18.27	24.36	55.74	395	Predominantly in HW
Human induced fire		21.63	26.27	52.10	395	Predominantly in HW
Construction materials		34.58	48.75	16.67	395	In all villages
Total	40.04		32.39	27.57	395

Conservation challenges from FGD

The key informants recognized the importance of the forest remnants to the local community as a source of firewood, construction materials, grasses for thatching and animal fodder, and livestock grazing areas. The discussants also believed that the forest coverage of the area is alarmingly shrinking, many wild animals are exterminated and the climatic conditions of the area is changing with time. They suggested that these problems are the consequence of irresponsible and unsustainable use of the natural forests by the local people. Firewood collection, farmland expansions, human settlement and overgrazing were the predominant biodiversity threats identified by the discussants. Exotic plantations, construction materials and human induced fire were the remaining conservation challenges raised during FGD. The discussants consider illegal land grabbing along the lake shores as a good opportunity than a threat to biodiversity.

Conservation challenges from field observations

Direct field observations confirmed the biodiversity threats mentioned by the respondents and key informants. Soil erosion, illegal land grabbing around lakeshores, insufficient information and monitoring, and household poverty due to small land size were additionally recorded conservation challenges to Wenchi biodiversity. Fuelwood collection, farming land expansions and overgrazing were relatively the most commonly observed biodiversity threats with varying intensity among the forest remnants. The area on the entry to Lake Wenchi and downstream forests is dominated by the matrix of Hagenia trees and absorbs maximum anthropogenic pressures as it is at proximate distance to the residential areas. It was constantly accessed by the local communities for fuelwood collection and cattle grazing. This area is also threatened by fragmentation and soil erosion (Supplemental B).

Qibate Forest was impacted by systemic firewood collection, overgrazing and extraction of forest products for other purposes. The claims by the local communities and some key informants that this forest is rarely exploited and local militias inspect the exploitations was false. In contrast, individuals were routinely observed carrying forest products intended for construction purposes and firewood during the study periods. Furthermore, grounded trees for firewood exploitation and construction uses were also encountered in the forest (Supplemental A). On average, more than ten firewood exploiters were seen in this forest during the wet season.

Albesa Forest was the second most exploited natural habitat, while Erica shrubland was the least. Firewood exploiters were either for home consumption or as a source of income by selling it to the urban residents who are in much need of it, particularly in the winter seasons. The former usually carry on their back to satisfy their household needs, while the latter were observed in numbers and assisted by children and donkeys. Lakeshore forest was also threatened by firewood extraction where firewood collections were aided by locally made boats. There was also an incident of charcoal production at the outskirts of Albesa Forest, which was the first observation in Wenchi highlands.

Conservation actions and opportunities

The respondents in Haro Wenchi village claimed that there is a relatively suitable conservation practices and an increase in the local community awareness after the establishment of ecotourism association in the area. There is also job creation in this village. According to these informants, cutting of live and indigenous trees, and exploitations of forest products for construction materials from Qibate Forest are prohibited as a means of forest conservation. They also suggested that local militias are responsible to inspect and control such malpractices.

The participants also recognized the needs of conservation priorities for the forest remnants through integrated conservation and development project options such as ecotourism. They also recommended that the regional and federal governments should develop conservation laws and directions, introduce initiatives of replanting certain areas, demarcate some of the areas either as forest priorities or reserve area, scale up environmentally friendly investments, create conservation awareness, and increase the local community involvements. Any conservation and ecotourism activity should be implemented in the ways that it can improve both the sustainability of the natural habitats and the living standard of the local community. The construction of terracing in the uplands through community participation was an encouraging effort in reducing the effects of erosion and fragmentation in the lower grounds. Such soil conservation activities should also be scaled up to the remaining areas.

The unique natural topographic beauty, rich flora and faunas, government led ecotourism development project, recent national and global recognitions of the area, and positive attitudes of the local people towards the habitats and its conservation were the potential biodiversity conservation opportunities in Wenchi highlands (Table 6). Some of these opportunities were shared among the forest remnants. However, most of them were limited to forest remnants located in Lake Wenchi watershed. For instance, Albesa Forest is not privileged to gain the recognition, and ecotourism project that other forest remnants cherished.

Table 6.

Possible conservation opportunities for Wenchi highlands biodiversity.

Opportunities	Details of these opportunities	Supportive evidences
Rich faunas and floras	Indigenous and endemic plantsSeveral endemic small mammalsColobus guereza and birds	Tufa et al. (2020)Shale et al. (2014)Legese and Bekele (2023)Direct observation
Unique natural topographic features	Lake WenchiMineral waters and hot springsMonastery and the hilly highland area covered with natural forests	Shale et al. (2014), Degefu and Schagerl, (2015), Tufa et al., (2020)Direct observation
Recent national and global recognitions	Best national tourism destination area in Oromia and Best tourist village of 2021 of UNWTO	Oromia Tourism CommissionUNWTO (2021)
National development project	One of the three nationally launched ecotourism projects	Tufa et al. (2022)National and regional medias
Local people positive attitudes	Most appreciated conservation efforts and willing to cooperate	Tufa et al. (2022)Interviews and questionnaires

Discussion

Local people in Wenchi highlands acquire different natural resources from the forest remnants either as recreation and enjoyment, income source, grazing area, source of construction materials or fuelwood. Countless forms of natural resource utilizations by the local community even from PAs is widely documented in different parts of Ethiopia (Yihune et al. 2009; Petros et al. 2016; Wale et al. 2017; Alemkere, 2018; Biset et al. 2019; Kiros & Bekele, 2021). Nonetheless, the unwise use of natural resources and other anthropogenic activities are responsible for a global biodiversity crisis (Frick et al. 2019).

Information obtained from the selected households, focus group discussion, local administrations and direct observations revealed that overgrazing, land-use changes, firewood collection, replacements of natives by commercial exotic plants, human induced fire, and illegal land grabbing were the major biodiversity threats in Wenchi highlands. Most of these threats were also reported across Ethiopia from both protected areas (Berihun et al. 2016; Petros et al. 2016; Mekonen et al. 2017; Kiros & Bekele, 2021) and outside these areas (Kasso & Bekele, 2014; Legese et al. 2019), and elsewhere (Munns, 2006; Imre & Derbowka, 2011). Several anthropogenic activities have threatened biodiversity through habitat loss and modifications (Musyoki et al. 2012; Kasso & Bekele, 2014; Legese et al. 2019). This is exacerbated by the rapid population growth, and the rise in demands of natural resources in most African countries including Ethiopia (Wale et al. 2017; Alemkere, 2018).

Land–use changes for agricultural production and human settlement are the main biodiversity threats in Wenchi highlands. This is in agreement with several reports in Ethiopia (Abune, 2000; Abrehe et al. 2020; Kiros & Bekele, 2021) and elsewhere (Mamabolo et al. 2020). The conversion of natural habitats for agricultural expansion is one of the most significant land-use changes in the world (Frick et al. 2019), and is primarily associated with higher crop productivity of these areas than farmlands (Kiros & Bekele, 2021). A very small land holding size of the study area farmers (0.5 ha per household) might force the farmers for additional farming areas (Shale et al. 2014).

Firewood collection is one of the major biodiversity threats in Wenchi highlands. Similar findings were also reported from different parts of Ethiopia (Legese et al. 2019; Abrehe et al. 2020). This is because the majority of the rural communities do not obtain electricity, and rely on fuelwood as sources of energy. Poor people also have no alternative income sources and use firewood and charcoal production as the best means of revenue generation (Legese et al. 2019; Kiros & Bekele, 2021). The proximity of urban areas to forested areas has also increased the intensity of forest destruction by fuelwood collection. Continuous livestock grazing is also a predominant biodiversity threat in Wenchi highlands. Overgrazing is known to affect the demography, population structure, spatial range of individuals and species, changing the community structure (Kasso & Bekele, 2014; Abrehe et al. 2020).

Human induced fire occurs in ericaceous belts of Lake Wenchi watershed. Burning was associated with the local communities’ agricultural farming land expansions. This result agrees with the finding of Horncastle et al. (2019). However, it was for pasture management, to discourage hazardous wild animals, to create human or livestock pathways, to reduce tsetse fly infestations and for wild honey collection in Gibe Sheleko National Park (Kiros & Bekele, 2021). Soil erosion associated with forest clearings, farming of uplands and infrastructural developments in the area has posed a serious existential threat to the forests and their biodiversity through fragmentation. This is exacerbated by the nature of soil of the area, which is easily erodible by a simple flood. A continuous livestock grazing of these habitats also further exacerbates this problem. Overgrazing by domestic livestock is the major cause of land degradation, and may affect the quality of the wildlife habitats (Horncastle et al. 2019; Umuziranengea et al. 2021). Conflict between the interests of livestock production and wild herbivore conservation is an increasing global challenge (Pozo et al. 2021).

In the study area, natural vegetation clearings and replacement by exotic commercial plants and the expansion of Eucalyptus spp. may have a negative impact on the vegetation structure of the area and its biodiversity. The same threatening factor was observed in Entoto Natural Park and Escarpments (Esayas & Bekele, 2011), and elsewhere across the world (Garcia et al. 2009; Kumar & Chhaya, 2015). According to Mekonen et al. (2017), wildlife resources of Ethiopia are under ongoing pressure due to replacement of the local varieties. The expansion of commercial exotic plants may be related to the rising market demands, and a better market pricing of these exotics than the native plants (Garcia et al. 2009). There was aggressive land grabbing and encroachments around the lakeshores. Similar problem has been reported by Degefu and Schargel (2015).

Insufficient information and poverty were among the challenges of biodiversity in Wenchi highlands. It is challenging to convince both the citizens and politicians about the need of conservation, and acquire funding with insufficient data (Hoffmann, 2021). According to Kideghesho et al. (2013), poverty is one of the root causes of biodiversity loss. Poverty affects funding of the sector, and forces the local people to use resources in unsustainable and ecologically damaging ways to cope up with it. It also restricts electric energy access and usage (Kideghesho et al. 2013).

Human–wildlife conflict was not such a major problem in the present study. This finding is against several reports from different parts of Ethiopia (Megaze et al. 2017; Kiros & Bekele, 2021), where human-wildlife conflict is a serious problem. The most likely reason for this might be the availability of a limited number of crop raiders. Crested porcupines and mole rats were the only reported crop raiders in the area. Other crop raiders, particularly medium to large-bodied mammals, are pushed out from the forest fragments. Yihune et al. (2009) have also reported less crop damaging impact of crop raiders due to their low population size in northern Ethiopia.

The majority of the respondents in the present study had a positive attitude towards the conservation of Wenchi highlands and their wildlife. Similar findings are documented by other reports from different PAs in Ethiopia (Biset et al. 2019; Kiros & Bekele, 2021), and Rwanda (Umuziranengea et al. 2021). Tufa et al. (2022) also documented similar findings from the current study area. A conservation friendly attitude of the public has a paramount importance for the success and sustainability of conservation efforts in a particular area. It is a golden opportunity that can be used as a potential resource for future conservation interventions. However, the willingness of farmers to conserve biodiversity is not sufficient in itself (Garcia et al. 2009).

The attitudes of the local community towards conservation efforts and wildlife are shaped by several intricate factors that the local people see and experience. It is principally based on the cost and benefit they experience (Tufa et al. 2022). Local people that obtain some benefits develop positive attitudes towards the conservation efforts (Biset et al. 2019; Kiros & Bekele, 2021). The positive attitudes of the locals in Wenchi highlands might be associated with 1) the absence of wildlife threats that could incur costs to them 2) a strategy they have used to avoid administrative hassles though they debark and selectively kill trees and systematically remove natural vegetation, and 3) the financial benefits they are gaining from the existing ecotourism association in the area.

Local people in Haro Wenchi in particular generate some benefits and incomes from the natural resources as a tour guide, renting horses, selling fuelwood, sharing ecotourism revenues and in the form of recreation and enjoyment. Local communities in Bale had also similar benefits (Petros et al. 2016). According to Wenchi Ecotourism Association policy, about 8% of the revenue and half of the entrance fee from ecotourism go to the community (Tufa et al. 2022). Similarly, there are cases when a percentage of the revenue from tourism is returned back to the community (Umuziranengea et al. 2021). Those individuals who had a negative attitude may consider the challenges associated with the scarcity of land for farming, human settlement and livestock grazing in the area and the prohibition of resource exploitation such as cutting of trees. Crop damage, livestock depredation, limitation of awareness, lack of benefit sharing may also lead people to develop negative perceptions towards conservation efforts (Megaze et al. 2017; Kiros & Bekele, 2021).

Wenchi highlands have striking and unique topographic features excelled by Lake Wenchi. The area also hosts diverse and unique plants and animals (Shale et al. 2014; Tufa et al. 2020, 2022; Legese & Bekele, 2023). According to Tufa et al. (2020), 90% of the woody plant species in Lake Wenchi watershed were indigenous, of which 16.7% were endemic to Ethiopia. Legese & Bekele (2023) also identified 17 small mammal species in these montane forests. More than half of these mammals were endemic to the country. There are also significant number of birds including the endemic Yellow-fronted parrot (Poicephalus flavifrons) and Blue-winged goose (Cyanochen cyanoptera), and many more that need further identifications. These make the area among the most popular ecotourism destinations in Ethiopia.

The government of Ethiopia has recently launched three nationwide ecotourism development projects which included Lake Wenchi and its adjacent landscape. This project has raised the reputation of the area both at national and international arenas. Consequently, the area was selected as the best national tourism destination area in the region by Oromia Tourism Commission, and the best tourist village of 2021 by UN world tourism organization in the same year (UNWTO, 2021). Such national and global recognitions can be used as an opportunity for the conservation of biodiversity in the area. The initiative has also led the government to take legal measures on illegal land grabbers along the lake shores that was a problem for a long time (Degefu et al. 2014; Degefu & Schagerl, 2015). On the other hand, development projects are also risky and may return unwanted results on biodiversity unless they are carefully planned and executed (Musyoki et al. 2012). Natural habitats in Wenchi highlands are not gaining equal conservation opportunities. Hereafter, any conservation practitioners and activities that are willing to conserve the natural environments should give equal opportunities for all the forest remnants.

Conclusion

Wenchi montane forests and their wildlife are severely threatened by several anthropogenic activities. Illegal land grabbing, overgrazing, overexploitation of natural resources, human settlement and farmland expansions, replacement of natives by exotics, and a seasonal burning of the ericaceous belt are some of the prevailing threats to Wenchi highland ecosystem, and the wildlife it hosts. However, recent global and regional recognitions of the area, positive attitudes of the local people, topographic beauty and rich flora and fauna, and ecotourism development project in the area are some of the promising opportunities that could serve as a springboard for its conservation.

Implications for conservation

The biodiversity in Wenchi montane forests is threatened by several human induced factors. This implies the need for urgent conservation priorities and actions in the area in order to safeguard these resources from local extinction. Furthermore, the presence of potential opportunities for the conservation of biodiversity of Wenchi highlands welcomes conservation initiatives and suggests their potential successes.

Supplemental Material

Supplemental Material - Assessment of challenges and opportunities for wildlife conservation in Wenchi highlands, central Ethiopia

Supplemental Material for Assessment of challenges and opportunities for wildlife conservation in Wenchi highlands, central Ethiopia by Kabeta Legese and Afework Bekele in Tropical Conservation Science

Footnotes

Acknowledgements

The authors are grateful to Wolkite and Addis Ababa Universities for their financial support, and Malela Shiferaw for his support during data collection. We are also indebted to acknowledge the local people and administrations for their participation and cooperation.

Declaration of conflicting interests

The author(s) declared no potential conflicts of interest with respect to the research, authorship, and/or publication of this article.

Funding

The author(s) received no financial support for the research, authorship, and/or publication of this article.

ORCID iD

Kabeta Legese

Supplemental Material

Supplemental material for this article is available online.

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Assessment of challenges and opportunities for wildlife conservation in Wenchi highlands,central Ethiopia

Abstract

Background and Research Aims

Methods

Results

Conclusion

Implications for conservation

Keywords

Introduction

Methods

Study area description

Ethical statement

Data collection

Data analyses

Results

Sociodemographic profiles

Responses on natural resource utilizations

Local community attitudes towards conservation

Conservation challenges from FGD

Conservation challenges from field observations

Conservation actions and opportunities

Discussion

Conclusion

Implications for conservation

Supplemental Material

Supplemental Material - Assessment of challenges and opportunities for wildlife conservation in Wenchi highlands, central Ethiopia

Footnotes

Acknowledgements

Declaration of conflicting interests

Funding

ORCID iD

Supplemental Material

References

Supplementary Material