Bale Mountains National Park

Country
Ethiopia
Inscribed in
2023
Criteria
(vii)
(x)
The conservation outlook for this site has been assessed as "significant concern" in the latest assessment cycle. Explore the Conservation Outlook Assessment for the site below. You have the option to access the summary, or the detailed assessment.

This property protects a landscape mosaic of extraordinary beauty that is shaped by the combined forces of ancient lava outpourings, glaciation and the dissection by the Great Rift Valley. It features volcanic peaks and ridges, dramatic escarpments, sweeping valleys, glacial lakes, lush forests, deep gorges and numerous waterfalls, creating exceptional natural beauty. © UNESCO

©IUCN/John Zulu

Summary

2025 Conservation Outlook

Finalised on
11 oct 2025
Significant concern
There are several current and potential threats and their cumulative impact on the site's values and associated attributes is considered high. Especially the hydrological system, Harenna forest, Erica forest and shrub, Gese grasslands, Afroalpine ecosystem, and Hagenia/Juniper woodlands are sensitive and being negatively impacted by agricultural activities, uncontrolled grazing, expansion of human activities and infrastructure, fire and unsustainable harvesting. While the General Management Plan (GMP) 2017-2027 outlines critical strategies, its implementation remains in its early stages, despite these escalating threats, with little on-the-ground mitigation. Limited funding, inadequate staffing, and the complexities of relationships with local communities are key barriers to progress, significantly hindering efforts to mitigate threats to the site’s OUV.

Current state and trend of VALUES

High Concern
With the continued increase of previously identified threats, most key attributes are of high concern and deteriorating. The property boundaries have remained porous, and human activities have escalated. Until these issues are addressed, the state of conservation is likely to deteriorate. Habitat fragmentation and loss due to human activities is affecting overall flora and fauna species richness. Ecosystems of the afroalpine plateaus and associated unique flora and fauna are also highly threatened by climate change. Although there are indications that the Ethiopian wolf and Mountain nyala populations in the property have stabilised over the past 4-5 years, agricultural and settlement expansion remain major threats. The range of the Bale monkey is decreasing rapidly due to ongoing habitat fragmentation and this is likely affecting a range of species, especially those associated with specific habitats.

Overall THREATS

High Threat
There are several current and potential threats and their cumulative impact on the site's values and associated attributes is considered high. Climate change will endanger a significant part of the unique Afroalpine flora, especially for Bale endemics. Furthermore, intensified human activities are further exacerbating the situation due to the expansion of human settlements, livestock grazing, agricultural activities and wood extraction. Especially the hydrological system, Harenna forest, Erica forest and shrub, Gese grasslands, Afroalpine ecosystem, and Hagenia/Juniper woodlands are sensitive and being negatively impacted by agricultural activities, uncontrolled grazing, expansion of human activities and infrastructure, fire and unsustainable harvesting. Another key threat is the loss of Traditional Ecological Knowledge and other knowledge systems with the relocation of local communities, which may impact the overall conservation of the site.

Overall PROTECTION and MANAGEMENT

Some Concern
The assessment of BMNP’s management system and governance reveals inadequacies in protecting its OUV. While the General Management Plan (GMP) 2017-2027 outlines critical strategies, its implementation remains in its early stages, despite escalating threats to the site. Key challenges, including agricultural expansion, settlements, overgrazing, and unsustainable resource harvesting, persist with little on-the-ground mitigation. The planned relocation of communities remains in the planning phase, further highlighting delays in execution and raising concerns regarding the just and equitable engagement of local communities. Failure to effectively protect the boundaries is undermining the OUV, casting doubts on the effectiveness of other programmes. Furthermore, management effectiveness cannot yet be properly evaluated, as many strategies remain either unimplemented or in the planning stages. The current plan is significantly behind schedule, still in its first cycle (2017-2020) while it should be in its final phase (2024-2027). Limited funding, inadequate staffing, and the complexities of relationships with local communities are key barriers to progress. The delay in taking decisive actions, particularly providing sufficient funding to place the World Heritage site on a sound footing, coupled with uncertainties in the timelines for the implementation of critical threat-abating strategies makes it difficult to establish realistic periods for delivering the various expected outcomes. In summary, most of the elements of a good plan are in place, however the key barrier to effective management is the implementation. High impact interventions can and should be carried out in the short-term to safeguard the ecological integrity of the site, including securing the boundaries to prevent further encroachment and illegal activities. However, without immediate, sustained, and well-supported interventions, the OUV of the site will continue to be degraded.

Full assessment

Click the + and - signs to expand or collapse full accounts of information under each topic. You can also view the entire list of information by clicking Expand all on the top left.

Description of values

Landscape mosaic of extraordinary beauty

Criterion
(vii)
Bale Mountains National Park (BMNP) contains a diverse array of dramatic landscapes, including volcanic peaks and sharp ridges, deep gorges, sweeping valleys, and glacial lakes. This creates an awe-inspiring scenery that hosts spectacular waterfalls, escarpments, and high-altitude plateaus in Africa, making it one of the continent’s most visually captivating and ecologically rich landscapes (IUCN, 2023; Atickem et al., 2010; Richman and Admassu, 2013; Ateneh and Temesgen, 2009; Hillman, 1988).

Steep altitudinal gradient that sculpts the land and vegetation

Criterion
(vii)
The layers of vegetation types in Bale Mountains National Park (BMNP) create a striking visual tapestry, unfolding along the park’s steep altitudinal gradient, from the lowland woodlands to the Afroalpine peaks. This transition in plant communities is not only ecologically significant but also visually captivating, offering a dynamic landscape of changing textures, colours, and atmospheric moods (IUCN, 2023; Asefa et al., 2020; Kidane et al. 2022; Miehe and Miehe, 1994; Lavrenchenko & Bekele, 2017; Marino et al. 2006). Key plant communities include: Lowland Dry Woodlands (1,500–2,500m), Moist Montane Forests (2,500–3,300m), Cloud Forests and Bamboo Groves (3,300–3,600m), Ericaceous Belt (3,600–4,000m), Afroalpine Meadows and Plateaus (4,000–4,377m).

Breathtaking hydrological features and sceneries

Criterion
(vii)
The park’s numerous glacial lakes, such as Garba Guracha (Black Lake), reflect the surrounding highland peaks, creating a striking visual spectacle. In the Harenna Forest, lush wetlands brimming with biodiversity add to the park’s mystical charm. BMNP is also the source of major rivers, including the Wabe Shebelle, Genale, and Web, which sustain ecosystems far beyond the park’s boundaries. Additionally, dramatic waterfalls cascading from the highland escarpments further enhance the park’s beauty. The Sanetti Plateau, with its vast, seasonally flooded Afroalpine bogs, glistens under the sun, offering a unique high-altitude landscape that completes the park’s stunning hydrological features (IUCN, 2023).

A geological and glaciological marvel

Criterion
(vii)
Bale Mountains National Park (BMNP) stands as a geological and glaciological marvel, its striations—boulder grooves etched into the Sanetti Plateau—offering a rare glimpse into Earth's ancient past (Gil-Romera et al. 2019). These enigmatic formations, shaped by unknown forces deepen the park’s geological and glaciological intrigues and significance. These striations support the understanding of past glaciation patterns and open new frontiers of research, transforming BMNP into a living laboratory.

Distinct ecosystems and high habitat diversity of outstanding importance for in-situ conservation of a diverse assemblage of species

Criterion
(x)
BMNP exhibits distinct ecological zones shaped by altitude, climate, and vegetation, ranging from lowland grasslands to Afroalpine moorlands. Each of these zones support a unique assemblage of species, many of which are endemic and adapted to the park’s altitudinal diversity (IUCN, 2023; Asefa et al., 2020; Miehe & Miehe, 1994; Mekonnen et al. 2012; NH, 2004; Atickem et al. 2010; Lavrenchenko & Bekele, 2017).

High degree of floral species richness and endemism

Criterion
(x)
The park is home to a great diversity of plant species, including 1,660 documented species of flowering plants, 177 of which are endemic to Ethiopia and 31 found exclusively in the Bale Mountains (IUCN, 2023; NH, 2004; Mekonnen et al. 2012). Of the 1,660 species, 177 are endemic to the Ethiopian Highlands, 31 of them (17.5%) are found only in the Bale Mountains. Over 337 plant species are considered medicinal plants, of which 24 are endemic (Lulekal et al. 2008; Yineger et al. 2008). There is a high species diversity among bryophytes (mosses, liverworts and hornworts) and research suggests that BMNP itself is home to some 1,660 vascular plant species. Of these, 177 are Ethiopian endemics (almost a third of all of Ethiopia’s endemic vascular plant species) and 31 of these are restricted to the Bale floristic region (NH 2004; Mekonnen et al. 2012). The understory of some of the lower forest areas of the Bale Mountains are also regarded as the most important site for genetic stocks of the wild variety of a major coffee species (Coffea arabica) (Zewdie et al. 2023).

High degree of faunal species richness and endemism

Criterion
(x)
The park hosts 78 species of mammals and 363 bird species. Of these, 20 mammal species, six bird species, 12 reptile species and 17 amphibian species are endemic (NH 2004; Williams et al., 2004; Asefa et al., 2006; Richman and Admassu, 2013). The Bale Mountains have the highest incidence of animal endemicity of any terrestrial habitat in the world (Hillman 1988; National Herbarium 2004; Williams et al. 2004). Out of the recorded mammals in the property, about a quarter are endemic to Ethiopia and of these, nearly half are restricted to BMNP (Richman and Admassu, 2013). The latest discovery is the endemic shrew (Crocidura afeworkbekelei) (Lavrenchenko et al. 2017). The highland areas of the BMNP are renowned for being home to the largest remaining populations of two of Africa’s most spectacular and most endangered large mammals, the Ethiopian wolf (Canis simensis) and the mountain nyala (Tragelaphus buxtoni). Ethiopian wolves are restricted to seven isolated mountain enclaves in the Ethiopian Highlands (Marino and Sillero-Zubiri, 2011). The Bale monkey (Chlorocebus djamdjamensis) is endemic to the Ethiopia highlands east of the Rift Valley (Bale Mountains and Sidamo Highlands) where the species occurs between some 2,300 and 3,300 m a.s.l. (Gippoliti et al. 2019). The giant mole rat (Tachyoryctes macrocephalus) is restricted to the Bale Mountains. Other species confined to the Ethiopian Plateau include six of the seven shrew species known (Crocidura thalia, C. glassi, C. lucina, C.bottegoides, C. harenna and C. afeworkbekelei (Lavrenchenko et al. 2016) and three mammalian species (Crocidura harenna, Cercopithecus djamdjamensis, and Mus triton) are endemics restricted to the Harenna Forest (Lavrenchenko et al. 2017). There are many other small mammal species, such as rodents, shrews and bats, several of which are endemic. Significantly, the rodent communities play a major role as a keystone species in the high-altitude ecosystems, performing important roles of cryoturbation (soil-mixing) and in food webs, not least as a main prey of Ethiopian wolves and many large raptors. Most experts agree that further discoveries of endemic small mammal species can be expected. There have been at least 363 bird species recorded in BMNP (Richman & Admassu, 2013; Lepage et al. 2020). BMNP is home to 27 endemic and near endemic species of Ethiopia and the Horn of Africa. Of these, six are endemic to Ethiopia including the blue-winged goose (Cyanochen cyanoptera); spot-breasted lapwing (Vanellus melanochepalus); yellow-fronted parrot (Poicephalus flavifrons); Abyssinian long-claw (Macronyx flavicollis), Abyssinian cat-bird (Parophasma galinieri); and black-headed siskin (Serinus nigriceps).
BMNP also harbours a noteworthy herpetofauna. It is well established that the Ethiopian Highlands are of particular importance for several endemic amphibian species with very narrow distributions, the Bale Mountains serving as a particularly good example. The 17 amphibian species that have been documented in the national park so far amount to about a quarter of all Ethiopian amphibian species. Of these, 11 are endemic to Ethiopia or even restricted to the Bale Mountains (National Herbarium 2004; Williams et al. 2004; Asefa 2007; Asefa et al. 2013). Five of the six endemic amphibian genera (Altiphrynoides, Spinophrynoides, Paracassina, Balebreviceps and Ericabatrachus) are endemic to BMNP (Largen & Spawls, 2006, 2011); the latter two constituting remarkable monotypic genera and the Bale Mountains are considered a globally important site for six frog species. As for reptiles, all the three snake species that have been recorded at altitudes above 2,800 m a.s.l. in Ethiopia (Psammophylax variabilis, Duberria lutrix and Pseudoboodon lemniscatus) are found in the Bale Mountains. In addition, an adder (Bitus harenna) only recorded in the Harenna Forest was relatively recently described (Gower et al. 2016). Two new species of forest chameleon were discovered in the national park in the recent past: the Harenna hornless chameleon (Trioceros harennae, Least Concern or LC) and the Bale two-horned chameleon (T. balebicornutus, NT) (Burgess et al. 2004). It is notable that the current knowledge of the herpetofauna of the Bale Mountains lizards remains incomplete.

Viable populations of rare and globally threatened species of outstanding universal value

Criterion
(x)
BMNP is vitally important for 13 globally rare and threatened mammal species that are vulnerable (VU), endangered (EN) or critically endangered (CR), according to the IUCN Red List (IUCN, 2023). Besides flagship species such as Ethiopian wolf, mountain nyala and Bale monkey, BMNP also hosts isolated and threatened populations of the endangered wild dog (Lycaon pictus) and the vulnerable black maned lion (Panthera leo) (Datson 2002; OARBD 2007; Mekonnen et al, 2020; Marino et al. 2006; Sillero-Zubiri & Marino, 2017).
The park is home to at least 29 globally threatened or endangered bird species (Redman et al. 2011; Lepage, 2020; Asefa et al. 2013). As of today, nine bird species are vulnerable (VU), twelve near threatened (NT), four are endangered (EN) and another four critically endangered (CR). The site also supports the migration of over 170 migratory bird species, such as wintering and passing raptors, including the Greater Spotted Eagle (indicating park's role in avian migration routes).
Critical genetic reservoir for wild forest coffee (Coffea arabica)
Bale’s montane forest is the native origin of Ethiopia’s only naturally occurring species of wild coffee (Coffea arabica), and one of the only two sites in the world where a naturally occurring wild population continues to be viable (Zewdie et al. 2023). The Bale Mountains coffee is the origin of domesticated Arabica coffee, from which 80% of the world coffee production comes (Urugo et al. 2025). This represents a globally important natural population of wild coffee genetic stock.
Richness of medicinal plants
The site is a source of numerous medicinal plant species. It is estimated that approximately 40% of all Ethiopian medicinal plant species are found in the Bale Mountains. So far, 337 medicinal plant species have been identified, of which 24 are endemic (National Herbarium, 2004; Lulekal, 2005; Yineger, 2005).
Great hydrological significance
Five major rivers (Web, Wabe Shebele, Welmel, Dumal, and Ganale) originate within BMNP, which is estimated to supply water and support the livelihoods of millions of people in Ethiopia, Kenya and Somalia. The rivers also sustain many aquatic and riparian ecosystems (IUCN, 2023).

Assessment information

High Threat
High threats including agriculture expansion, livestock overstocking, human settlements, wood extraction, and fire are spread across the site, including in the park's hydrological system, the Harenna forest, the Erica forest and shrub, the Gese grasslands, the Afroalpine, and Hagenia/Juniper woodlands. These threats have generally been on the rise since the last management plan of 2006. Rabies and canine distemper is rated as a significant threat to the survival of the Ethiopian wolf. Other threats such as unsustainable harvesting of non-timber natural resources e.g. bamboo, grass, coffee; poaching, persecution, human disturbances, and impacts from infrastructure development e.g. quarrying, building, road kill, and litter are also increasing. Therefore, the values and associated attributes are significantly impacted by these threats.
Residential Areas
(Expanding human settlements)
Very High Threat
Inside site
, Throughout(>50%)
Outside site
The threats from human settlements and associated resource use have been increasing over the past decades (EWCA 2017 & 2024; Gulte et al. 2023). Existing settlements are growing and new settlements are appearing in previously unsettled and environmentally sensitive areas. The emergence of new settlements is associated with the rapid immigration from the surrounding lowlands (Jacobs and Schloeder, 2001; Farm Africa, 2008). Human settlements within the protected area is today among the 3 most severe threats to the OUV of the site (BMNP 2020 Management Effectiveness Assessment). It is estimated that there are over 3,000 households in the park accounting for roughly 20,000 permanent people (Gulte et al. 2023) and 20,000 seasonal resource users. Hence over 40,000 people live within the park’s boundaries, increasing pressure on the natural resources of the area and diminishing natural habitats of various animals (BMNP, 2025).

By 2017, the threats were rated high and increasing in Harenna forest, Erica forest and shrub zone, Afroalpine, and Hagenia/Juniper woodlands; and moderate and increasing in the hydrological system. The threat to the Mountain nyala and Ethiopian wolf were rated high and these threats are reported to be roughly comparable to those in the 2006 BMNP GMP (EWCA, 2017). As noted, the threats have been increasing since the last General Management Plan of 2006-2017.

The current management plan (ECWA, 2017) provides a summary of the impacts arising from settlements, including: land conversions and clearance of forests and grasslands leading to the loss of critical habitats for endemic species like the Ethiopian wolf and Mountain nyala; habitat fragmentation due to roads, paths, and human dwellings; increasing livestock into the park, leading to overgrazing and habitat degradation. This depletes vegetation, erodes soils, and reduces the availability of forage for native herbivores. Furthermore, human activities have led to wildlife displacement and direct hunting of wildlife for food or income, targeting species like the Ethiopian wolf and Mountain nyala, both of which are already endangered.
Livestock trampling around settlements near water sources contributes to water pollution and sedimentation while settlements increase interactions with wildlife, often resulting in retaliatory killings when wildlife preys on livestock or damages crops.
Furthermore, settlements have led to the introduction of invasive plant and animal species, which compete with native species and disrupt ecological balance.
Annual & Perennial Non-Timber Crops, Terrestrial Animal Farming, Ranching & Herding
(Agricultural expansion and livestock grazing)
Very High Threat
Inside site
, Throughout(>50%)
Outside site
Expansion of agriculture, including in the most fragile habitats deep inside the park has been a major threat to the ecological integrity of BMNP for several decades.
Farmers typically grow barley, wheat, potatoes, highland fruits (apple, pear), maize, coffee, and other subsistence crops, which are well-suited to the high-altitude climate. Agricultural activities have increased in all areas of the park (EWCA 2017), including in remote and inhospitable areas of the Afroalpine and Harenna forest. In the mid-2000s a 700-hectare area, Aboye, was illegally cleared for agriculture. Livestock grazing is also a growing threat. An estimated 725,000 livestock graze the afro-alpine habitats and 25,000 livestock graze in the Harenna Forest during peak seasons (IUCN, 2023). Within the Web Valley area of the park, where the Ethiopian wolf is concentrated, cattle density is estimated at 250 per square kilometre, leading to the degradation of the Afroalpine ecosystem on which the wolf’s prey depend (Yimer, 2023).

Farmlands overlap with key wildlife habitats causing ecosystem and habitat fragmentation; disrupting ecosystem processes and altering ecological balance; encroaching on habitats for key species, including those of rare, endangered and endemic species; causing and accelerating habitat degradation and biodiversity loss; increasing risks for introduction of invasive species; increasing fire risks and incidences of human-wildlife conflicts. By 2017, the threats were rated high and increasing in hydrological systems, the Harenna forest, Erica forest and shrub zone, and Hagenia/Juniper woodlands; and moderate and increasing in the Afro-alpine zone. Agriculture related threats to the Mountain Nyala were rated high and increasing, and medium and increasing for the Ethiopian wolf (EWCA, 2017). As these threats are caused by increasing human activities which has been increasing due to porous boundaries and poor law enforcement (EWCA 2025), the negative impact on the OUV of the property is considered very high.

According to Muhammed & Elias (2021) from 1985 to 2017 grassland, Erica, forestland, and afro-alpine decreased by 9.36 %, 0.26 %, 0.06 %, and 0.01 %, respectively, whereas, farmland increased by 43.67 %. Core Protection Zones (CPZ) in the BMNP have been established to reduce grazing pressure. Since 2020, a total area of 82,882 hectares (38%) has been included in the CPZ area. Along with the General Management Plan and its Interim Settlement and Grazing Management Program, these measures aim to target unsustainable grazing in the park (State Party of Ethiopia, 2024).
Mining & Quarrying
(Quarrying)
High Threat
Inside site
, Widespread(15-50%)
Outside site
Quarrying activities within BMNP have notably increased over the past several decades, particularly in the Gese grasslands and Afroalpine zones leading to significant environmental impacts (EWCA, 2017). A study analysing red ash quarry sites within the park revealed that between 1967 and 2023, the total net surface volume of two major quarry sites decreased by approximately 503,721 ± 27,970 m³ and 368,523 ± 30,003 m³, respectively. The excavated areas expanded by 53,147 m² and 45,297 m² for the two sites. This extraction has led to habitat loss, including reductions of approximately 476,860 m² of Afro-Alpine vegetation, 403,806 m² of ericaceous vegetation, and 493,222 m² of Afromontane forest, adversely affecting species diversity and density (Muhammed et al. 2024). Negative impact on Mountain nyala has also been noted. Other negative impacts from quarrying activities are: clearance of large areas resulting in habitat loss; removal of rocks and soil alters the landscape, fragmentation of ecosystems and the destruction of breeding and foraging grounds; removal of vegetation makes the land vulnerable to erosion; produces dust that affect air quality; noise from heavy machinery and blasting disturb sensitive wildlife species; possible ground water contamination; human activities associated with quarrying drive wildlife away from their habitats; open pits and quarries can become traps for animals, leading to injury or death; creates disturbed areas that are susceptible to invasion by non-native plant species; access roads facilitates easy access to otherwise remote areas (Endalew et al. 2019; Carabassa et al. 2020; Muhammed et al. 2024).
Roads, Trails & Railroads, Utility & Service Lines
(Construction of roads and other public infrastructure )
Low Threat
Inside site
, Scattered(5-15%)
Outside site
Roads introduce multiple ecological and environmental challenges during their construction and use. Construction requires clearing large areas of vegetation, resulting in habitat loss and a reduction in biodiversity; soil excavation leads to erosion, particularly on steep terrains in the park; roads also cause ecosystem and habitat fragmentation, disrupting the natural movement of wildlife, such as the Mountain nyala and Ethiopian wolf; they alter landscape stability resulting in landslides or the collapse of loose soil during heavy rains; affect natural water flow in some areas; facilitate the spread of invasive plant species; introduce a new threats such as vehicle-wildlife collisions resulting in road kills; heavy traffic causes air, noise and light pollution, which can stress wildlife and disrupt natural behaviours and even lead to habitat abandonment; some species such as baboons are attracted to roads due to food scraps or roadside vegetation, increasing their risk of vehicle collisions. Roads also create "edge" effects that alter microclimates and increase vulnerability to invasive species. According to Muhammed et al. (2024), excavation and gravel road construction has contributed to the degradation of the Afro-Alpine ecosystem, especially the endemic Lobelia rhynchopetalum.

The road from Addis Ababa to Goba, runs through the BMNP and another road runs through both the Sanetti Plateau and the Harenna Forest. Service utility roads also exist to access telecommunication infrastructure on several mountain tops. Some pass through ecologically fragile areas (EWCA 2017). The development of gravel roads within BMNP has resulted in substantial habitat loss. For instance, major gravel road construction inside the park led to the reduction of approximately 48 ha of Afro-Alpine vegetation, 40 ha of ericaceous vegetation, and 49 ha of Afromontane forest, adversely affecting species diversity and density. Up to ten truckloads are transported daily, leading to bare soil exposure, erosion, altered topography, and changes in drainage patterns, making vulnerable areas susceptible to flooding (Muhammed et al. 2024).
Hunting, Collecting & Controlling Terrestrial Animals
(Poaching)
Other targeted species names
Tragelaphus buxtoni, Canis simensis
Data Deficient
Inside site
, Scattered(5-15%)
Outside site
Poaching of the Mountain nyala and the Ethiopian wolf is reported as a low threat in the current management plan (EWCA, 2017), however the extent to which this threat affects the site's OUV is uncertain. One reason for poaching is human-wildlife conflict due to the increasing trend of livestock predation by various animals (spotted hyena, olive baboon, common jackal, aardvark, genet, Ethiopian wolf, lion, and leopard) (Sebsibe, 2022).
Gathering, Harvesting & Controlling Terrestrial Plants & Fungi, Logging, Harvesting & Controlling Trees
(Unsustainable natural resource use)
High Threat
Inside site
, Widespread(15-50%)
Outside site
Wood extraction is increasing in nearly all the ecosystems of the park (EWCA, 2017) resulting in loss of biological diversity. Such illegal activities have many negative impacts on the OUV of the site as they open the affected areas to other activities such as grazing and expansion of agriculture, which already pose a high threat. Illegal activities like logging, collection of grasses and medicinal plants and coffee harvesting are reported as threats in the current management plan. Wood extraction is a significant threat in many ecosystems including in the Erica forest and shrub where it is rated high, and moderate in Harenna forest, Afroalpine zone and the Hagenia/Juniper woodlands. It is also a significant threat to the Mountain nyala (ECWA, 2017). However, these threats are reported to be roughly comparable to those in the 2006 management plan for BMNP. In 2020 a buffer zone was established to safeguard the property through community-based natural resource management schemes (IUCN, 2023). Furthermore the management authority is implementing Park Cooperative Agreements with Participatory Natural Resource Management Cooperatives (PNRM). Since 2020, 32 agreements with PNRM cooperatives were established to engage local communities as conservation partners and actively involve communities in monitoring programmes through training programmes, workshops and resource-sharing initiatives (State Party of Ethiopia, 2024).


Conflict, Civil Unrest & Security Activities
(Tribal conflicts)
Low Threat
Inside site
, Scattered(5-15%)
Outside site
BMNP has been a focal point of tribal conflicts due to a complex interplay of historical grievances, competition over natural resources, political dynamics, and conservation restrictions. The park’s overlap with traditional pastoralist and agricultural communities has resulted in frequent disputes over land and resource use (Hagmann & Mulugeta, 2008, Kelboro & Stellmacher, 2012; Mekonnen et al., 2020), exacerbating ethnic and political tensions (Hagmann & Mulugeta, 2008, Tadesse & Kotler, 2016, Dereje & Hoehne, 2018). BMNP’s designation as a protected area prohibits traditional grazing and agricultural expansion, leading to competition and friction between local communities and park authorities (Kelboro & Stellmacher, 2012; Mekonnen et al., 2020).

Impacts of such conflicts include threats to biodiversity resulting from encroachment, land disputes, and retaliatory poaching contribute to habitat destruction and biodiversity loss (Sillero-Zubiri & Marino, 2017); weakening park management thus hindering conservation efforts, making it difficult for rangers and researchers to operate effectively (Mekonnen et al., 2020), and causing disruptions to the ecotourism industry, a vital source of revenue for conservation and local livelihoods (Tadesse & Kotler, 2016).
According to the nomination dossier and state of conservation reporting, the State Party is encouraging the voluntary relocation of permanent settlers from BMNP based on a community engagement plan that ensures FPIC processes are respected (State Party of Ethiopia, 2024; IUCN, 2023) to address unsustainable natural resource use.
Pathogens
(Disease spread, especially rabies and CDV)
High Threat
Inside site
, Widespread(15-50%)
Outside site
Diseases pose a significant threat to several species in BMNP including Ethiopian wolves, Mountain nyala and amphibians. Disease surveillance and management currently undertaken by the EWCP confirm that at least five outbreaks of rabies and at least three, possibly four outbreaks of canine distemper have occurred in the Bale Ethiopian wolf population in the last 25 years. Due to the increase in the domestic dog population, the risk of diseases like rabies and Canine Distemper Virus (CDV) being transmitted to the wolves has been raised significantly. In 2010, two-fifths of the park’s wolves died from disease, and in 2019 70% died from canine distemper, according to the park authority (Yimer, 2023). These outbreaks, when not controlled, have caused mortality of up to 76% in affected subpopulations. Pathogens are transmitted from the rodents, carcass, stray dogs, humans and the environment, especially water bodies. As human encroachment continues, the likelihood of the emergence of new pathogens to wild animal populations is high (Jilo et al. 2023).

Population viability analyses suggest that outbreaks of this severity and frequency substantially increase the probability of extinction among Ethiopian wolves. Fortunately, over the past four years, there has been a stabilization of the population, which according to the State Party is attributable to ongoing vaccination efforts, which include comprehensive initiatives such as oral rabies vaccinations for wolf packs throughout the Bale Mountains, as well as a targeted canine distemper vaccination trials undertaken with select packs (State Party of Ethiopia, 2024). However, possible impacts of vaccination of wolves include artificially suppressing disease pressures, reducing the natural selection for disease-resistant individuals, potentially weakening long-term population resilience. Long-term use of vaccines could lead to pathogens evolving resistance, reducing the effectiveness of vaccination programs.

Fire & Fire Management
(Increase in uncontrolled fires)
High Threat
Inside site
, Widespread(15-50%)
Outside site
Frequent uncontrolled fires in BMNP pose severe threats to its ecosystems, biodiversity, and conservation efforts, including habitat destruction and biodiversity loss in forests, grasslands, and shrublands. Fire-sensitive species, such as the endemic giant lobelias and Hagenia trees, are particularly vulnerable. Other fire-associated threats include exposing soil to erosion; wildlife mortality; hindering regeneration; changing ecosystem structure and function by promoting fire-tolerant species, including invasives. Fire is the most frequent disturbance in the Ericaceous Belt (ca 3000–4300 m.a.s.l.), one of the most important plant communities of tropical African mountains. Through resprouting after fire, Erica establishes a positive fire feedback under certain burning regimes. However, present-day human activity in the Bale Mountains of Ethiopia includes fire and grazing systems that may have a negative impact on the resilience of the ericaceous ecosystem (Gil-Romera et al. 2019).

Large fires have increased in frequency, attributed to lack of fuel breaks and the fact that fires today are ignited in a more uncontrolled manner later in the dry season (Johansson et al. 2019). Over the last 30 years, the scope of fires increased from 210 ha to 12,825 ha. About 84% of the recent fires within the BMNP, burnt 60% of the “Ericaceous belt”, the major water catchment area of the Bale Mountains massif. Most fires were human induced. A declining water percolation, increasing runoff, rivers pollution, death and migration of wild life, burnt soil up to 15 cm depth, shrinking forest size were mentioned as major consequences. A continued forest fire may lead to the devastation of the entire hot spot, signifying the urgent need to design an integrated forest fire management plan (Belayneh et al. 2013). Although fire is a natural feature in some of the habitats, in recent years, the combination of hotter extended dry seasons and increased fires set by people is causing unsustainable habitat destruction. Pressure for grazing land, honey harvesting and slash and burn cultivation are all associated with fires. The 2019 dry season fires burned significant areas of critical habitats, including in the Harenna forest (RRF, 2022). In response to wildfires in Bale Mountains National Park in Ethiopia, the Rapid Response Facility (RRF) granted $14,625 to Frankfurt Zoological Society to develop more effective fire-fighting and fire prevention capacity (RRF, 2022).

Fire threat was rated high in the Harenna forest and Erica forest and shrub zone, moderate in Gese grass-lands and low in the Afroalpine zone in 2017. They also pose medium level threat to the Mountain nyala, and low level threat to the Ethiopian wolf (EWCA, 2017).
Changes in traditional ways of life and knowledge systems that result in negative impact
(Loss of Traditional Ecological Knowledge Systems)
Data Deficient
Inside site
, Throughout(>50%)
Loss of traditional ecological knowledge and traditional natural resource management systems such as the traditional pastoral transhumance system (Godantu) of Oromo pastoralists, through the removal of local communities, can create conditions similar to the tragedy of the commons. Loss of the long-standing cultural or traditional practices that sustainably manage natural resources, leaves ecosystems vulnerable to exploitation by external actors who lack the same vested interest in conservation. Some key threats include: loss of multiple unique and complex mixes of traditional natural resource management strategies adapted to particular natural and social conditions; loss of traditional values that work together to safeguard natural and cultural heritages; loss of culturally mediated means of managing, conserving and utilizing specific natural resources; loss of traditional knowledge, practices that are based on cultural and religious values, knowledge systems, myths, taboos, rules, and beliefs that relate to nature and its resources, devotion to future generations, ethical regard for nature, and commitment to community among people. The forced removal of local communities from their traditional lands for national parks causes profound negative impacts. It severs cultural ties, erodes identity, and disrupts traditional ecological knowledge systems. Social cohesion weakens as communities face dispersal, internal conflicts, and the breakdown of traditional governance structures. Economically, displacement leads to the loss of livelihoods and increased poverty, while socially, it fosters trauma, disempowerment, and marginalization. Cultural practices and languages tied to the land often diminish or disappear, and the community's stewardship of ecosystems, critical for biodiversity and climate stability, is lost, often resulting in environmental degradation. Additionally, these displacements breed long-term mistrust of conservation authorities and governments, exacerbating tensions and resistance. Relocation plans must address these issues to ensure long-term conservation of the park’s OUV.
Invasive Non-Native/ Alien Species
(Invasive plants)
Invasive/problematic species
Parthenium hysterophorus
Xanthium strumarium
Argemone ochroleuca
Low Threat
Inside site
, Localised(<5%)
Outside site
Threat from invasive alien species do not seem to be spread widely in the property. The current management plan identifies the Gese grasslands as the only zone with medium level threats from invasive alien species (EWCA, 2017). A study focusing on invasive plant species in and around Bale Mountains National Park (BMNP) (Mahmud et al. 2024) identified 12 invasive plant species, with Parthenium hysterophorus, Xanthium strumarium, Argemone ochroleuca, and various Acacia species being highly prevalent. These invasive species were found to heavily infest roadsides and arable lands. The study highlighted the need for increased awareness and control measures to prevent further spread into the World Heritage site. Invasive species have significant negative effects on biodiversity, ecosystems, livestock, crops, and human health (Mahmud, et al, 2024). They have the potential to outcompete native species, alter habitats, and disrupt ecological processes. Fast-growing invasive plants such as Parthenium hysterophorus and Xanthium strumarium replace native vegetation, reducing food sources for pollinators and herbivores. Kidane (2022) also noted the introduction of exotic plant species such as Eucalyptus and Cupressus along the main road, villages, and towns, which threatens biodiversity. Therefore, there is a need to study the impact of the introduction of alien species in the area. Some particularly invasive grasses increase wildfire frequency and intensity, leading to habitat destruction. In addition, invasive animals and plants introduce new diseases, threatening native wildlife populations (Mussa et al., 2018).
Problematic Native Species
(Hybridization of wild and domestic species)
Data Deficient
Inside site
, Throughout(>50%)
Occurrences of hybridization of Ethiopian wolf with domestic dog and hybridization of the endemic Bale monkey with the grivet (Chlorocebus aethiops) and the vervet monkey (Chlorocebus pygerythrus) have been noted, attributed to habitat changes (Mekonnen 2018). The extent of hybridization and impact on the site's OUV is unclear.
Water-borne & other effluent Pollution
(Runoff from dissolved fertilizers and pesticides from farms)
Data Deficient
Inside site
, Extent of threat not known
The expansion of agricultural activities within and around BMNP leads to the use of fertilizers and pesticides. The use of such chemicals in natural ecosystems can have significant and often detrimental impacts on biodiversity, soil health, and water quality. Their accumulation can reduce soil microbial diversity. Runoff into rivers, lakes, and wetlands alter aquatic ecosystems, and disrupt natural food chains. Long-term use can lead to soil acidification, which affects nutrient availability, microbial activity, hinder plant growth, and reduce ecosystem productivity.
Water-borne & other effluent Pollution, Garbage & Solid Waste
(Plastic pollution and household waste)
Data Deficient
Inside site
, Extent of threat not known
Waste produced by tourism activities and local communities living within the park may be directly ingested by animals or leach pollutants into rivers and streams, affecting aquatic ecosystems and downstream communities, others may impact on soil fertility. Some materials that are relevant include plastic bottles and packaging; household trash generated by communities living within the park; plastic bags used for carrying or storing agricultural products; construction debris such rubble, wood, and metal scraps from infrastructure projects; wire traps abandoned by poachers.
Air-borne Pollutants
(Smoke and dust)
Very Low Threat
Inside site
, Scattered(5-15%)
Air-borne pollution is a low threat, originating from slash-and-burn practices, smoke from burning of waste in local settlements, dust and exhaust from vehicles using park roads, smoke from forest fires when they break out. Smoke and other particulates settle on plant leaves, reducing photosynthesis and growth. They may also cause respiratory problems to some species that may be sensitive to such pollutants.
High Threat
The impact of climate change has not been studied in depth and is among the priority research activities in the current management plan. However, just like in any other mountainous ecosystems, climate change increases vulnerabilities of key attributes due to the impact from wildfires, invasive alien species, diseases, extreme events, among others. Biodiversity loss, particularly of endemic species is likely to be a significant challenge for the park's management. With regard to the widespread use of oral and parenteral vaccinations on the population dynamics of the Ethiopian wolves, the long-term effect remains unknown. However, any intervention on an endemic species that is highly endangered remains an issue of concern. Short and long-term impact of predator-prey relationships due human activities also need to be assessed. According to the current management plan direct predation and attacks by dogs pose a threat to a number of wildlife populations, including rodents, mountain nyala, Menelik’s bushbuck and other antelope species (especially young calves) in the Gese grasslands and Hagenia/Juniper woodlands. Dogs also pose a threat to Ethiopian wolves though competition as rodent predators and to other scavengers like hyena and vultures through consumption of wildlife carcasses. Changes in vegetation composition and structure is likely to introduce complex food-web and food chain factors which may not be obvious at this stage. Another potential threat is the social, cultural, economic and environmental impact of relocation of local communities that have deep historical, cultural, and spiritual connections with and livelihood dependence on park ecosystems and resources.
Changes in Physical & Chemical Regimes, Changes in Temperature Regimes, Changes in Precipitation & Hydrological Regime
(Climate change)
High Threat
Inside site
, Throughout(>50%)
Outside site
Climate change will endanger a significant part of the unique Afroalpine flora, especially Bale endemics (Kidane, 2022). The Afroalpine plateau is threatened by climate change, including the assisted expansion of some prominent cover classes such as Ericaceous vegetation, threatening mass extinction of the unique Afroalpine endemic flora and fauna. The impact of climate change has not been studied comprehensively in the site, and is among the priority research activities in the current management plan. However, it is clear that the possible impacts of climate change are interlinked with wildfires, invasive alien species, wetland conservation, biodiversity loss and local livelihoods.
Biological System Management
(Impact of widespread use of oral and parenteral vaccinations on the population dynamics of the Ethiopian wolves )
Data Deficient
Inside site
, Extent of threat not known
The impact on population dynamics of widespread use of oral and parenteral vaccinations in Ethiopian wolves is flagged as a research priority in the current management plan, highlighting the need to finalize any further trials required to test efficacy and safety of oral and parenteral vaccines against rabies and CDV in wolves (EWCA, 2017).
Terrestrial Animal Farming, Ranching & Herding
(Changes in predator-prey dynamics in the ecosystem)
Data Deficient
Inside site
, Extent of threat not known
Short and long term impact of predator-prey relationships due to habitat changes caused by human activities needs to be monitored carefully. According to the current management plan, direct predation and attacks by dogs pose a threat to a number of wildlife populations, including rodents, mountain nyala, Menelik’s bushbuck and other antelope species (especially young calves) in the Gese grasslands and Hagenia/Juniper woodlands. Dogs also pose a threat to Ethiopian wolves though competition as rodent predators and to other scavengers like hyena and vultures through consumption of wildlife carcasses (EWCA, 2017).
Changes in traditional ways of life and knowledge systems that result in negative impact, Identity/social cohesion/ changes in local population and community that result in negative impact
(Overall impact of relocation of local communities with deep historical, cultural, and spiritual connections with and livelihood dependence on park ecosystems and resources)
Very High Threat
Inside site
, Throughout(>50%)
The current management plan clearly states that addressing the high-ranking threats facing BMNP depends on the successful implementation of the Interim Settlement and Grazing Management Programme. It acknowledges that reducing settlement and resource use within BMNP will take time and that the current situation cannot be controlled immediately. Therefore, a phased approach is proposed (EWCA, 2017).

The plan further notes: “The areas of BMNP free of settlement and grazing will be expanded over time, allowing BMNP management systems to be developed and providing assistance to local communities to help them sustain their livelihoods within their own lands outside the park.” BMNP has not yet included the payment for ecosystem services project due to uncertainty around settlement relocation plans and the challenges of ensuring these plans meet social responsibility standards for carbon payments. However, efforts must be made to ensure BMNP receives payments while preventing leakage into the park from this scheme. This uncertainty significantly undermines confidence in the effectiveness of the proposed measures to protect the Outstanding Universal Value (OUV) of the property.
Involvement of stakeholders and rightsholders, including indigenous peoples and local communities, in decision-making processes
Some Concern
The governance of the BMNP under the General Management Plan (GMP) 2017-2027 has established a strong foundation for conservation and community engagement. The GMP recognizes the importance of stakeholder involvement and has fostered dialogue through cooperative agreements, participatory grazing zones, and the establishment of a Park Advisory Committee (PAC). A rights-based approach will be used to ensure that local communities are consulted in key decisions. Mechanisms to ensure Free Prior and Informed Consent (FPIC) and a Grievance Redress Mechanism (GRM) have been developed to safeguard community interests. Core Protection Zones (CPZs) and resource management regulations have been introduced to ensure ecological sustainability. All these plans aim to integrate conservation into local development strategies, with goals to balancing biodiversity protection with community needs (State Party of Ethiopia, 2024).
However, significant challenges remain in fully realizing these goals. Community participation in the development of the management plan was limited, leading to dissatisfaction and a sense of exclusion among local residents (Yimer, 2023). Although participatory forums exist, conflicts persist over access to resources such as fuelwood, grazing land, and farmland, which are vital to community livelihoods and fair benefit sharing (Gulte et al. 2023). In an interview carried out in Oct 2023, some long term residents indicated they had heard of relocation, but were unwilling to relocate, irrespective of the amount of compensation promised (Yimer 2023).
Institutional weaknesses further complicate governance efforts, with inconsistent enforcement of regulations and limited financial and technical capacity to implement the GMP effectively. Economic incentives for conservation, such as ecotourism and alternative livelihoods, have yet to be fully developed, leaving many local people uncertain about the benefits they stand to gain. Additionally, while gender equity is not explicitly addressed in the GMP, there is potential for greater inclusion of women in governance structures and economic programs linked to conservation.
A recent study reported that park management and government authorities use their authority to decide how local communities should participate in Bale Mountains National Park management initiatives (Gulte, et al, 2023). Such top-down approaches fail to adequately involve local communities in the decision-making processes, and have the risks of escalating the current threats, ultimately threatening its UNESCO World Heritage status. The park’s future depends on inclusive governance that empowers communities as conservation partners.
Legal framework
Mostly Effective
The site benefits from a strong legal framework that provides a high level of protection, ensuring its recognition as a World Heritage site is upheld. The Ethiopian Wildlife Conservation Authority (EWCA) manages the park under Proclamation No. 575/2008, which establishes its mandate, and Proclamation No. 541/2007, which governs national wildlife conservation. The park is further protected under the Council of Ministers Regulation No. 338/2014, officially gazetted in Negarit Gazet 338/2014, aligning it with IUCN Protected Area Category II standards. Additionally, BMNP’s management strategies conform to broader national frameworks, including the National Biodiversity Conservation and Research Policy (1998), the National Biodiversity Strategy and Action Plan (2005), the Environmental Impact Assessment Proclamation (No. 300/2002), and the Wildlife Development, Conservation, and Utilization Policy (2005) and Proclamation (Negarit Gazet 163/2008). These laws and policies emphasize sustainable resource use, biodiversity conservation, and the requirement for Environmental Impact Assessments (EIAs) before development projects are allowed.
However, despite this comprehensive legal foundation, several challenges undermine its effective integration into governance and management. While BMNP’s ecological and outreach strategies align with federal and regional legislation, lack of coordination between stakeholders has resulted in conflicting development interests. For instance, various agencies have initiated permanent infrastructure projects within the park, such as roads and telephone towers, without consulting BMNP management or conducting EIAs (ECWA, 2017). These activities directly contravene existing government policies and legislation that prohibit such development within protected areas. The absence of a cohesive enforcement mechanism weakens the legal framework’s ability to maintain the park’s Outstanding Universal Value (OUV).
Governance arrangements
Some Concern
The Ethiopian Wildlife Conservation Authority (EWCA), established under Proclamation No. 575/2008, is responsible for overseeing BMNP, providing a strong legal foundation for conservation. The park administration operates through a dedicated management office, supported by ranger outposts and mobile units to facilitate law enforcement, biodiversity monitoring, and community engagement. Roles and responsibilities are outlined through legal mandates and stakeholder consultations, with the aim to create a governance system based on shared responsibility. A key initiative in this regard is BMNP’s Outreach Programme, which aims to strengthen relationships with local communities and stakeholders, guided by principles that emphasize mutual respect, open communication, community participation, benefit-sharing, and coordination among stakeholders. According to the GMP, transparency and access to information are fundamental to the park’s governance, ensuring that stakeholders and rightsholders have a clear understanding of its management decisions. The park’s Management Plan and Strategic Plan (SP) provide detailed insights into the state of biodiversity, historical influences, and ongoing conservation challenges.
Given the complex socio-economic and environmental dynamics surrounding a World Heritage site, BMNP has established a dispute resolution mechanism to address grievances and conflicts, to ensure that disputes related to conservation policies, land use, and resource management are resolved through participatory and equitable processes. Additionally, BMNP has developed communication strategies that facilitate engagement with local communities, government agencies, non-governmental organizations, and researchers, to foster cooperation and long-term commitment to conservation efforts.
A critical aspect of BMNP’s governance defined in the GMP is its adaptive management approach, which follows a structured three-year planning cycle. This cycle is intended to integrate implementation, monitoring, and evaluation, allowing for continuous refinement of conservation strategies to ensure that BMNP remains resilient and responsive to ecological, social, and economic changes, in line with UNESCO’s principles for heritage conservation. However, the established governance structure has not translated into effective management actions. The property still faces severe challenges and threats, which, according to the GMP, are severe and increasingly acute and are likely to result in further loss and degradation of biodiversity and ecosystem services in the longer term (EWCA, 2017). The afro-montane and the afro-alpine regions have been subject to major habitat loss and degradation for many decades across most of its once vast distribution. Agricultural expansion, livestock overstocking and settlements are the most severe threats affecting the property along with the conversion of forests and grasslands to farmland, unsustainable harvesting of timber and other species (e.g., bamboo, coffee) and excessive levels of livestock.

All these and other pressures lead to the conclusion that the governance structure has not been effective in addressing the challenges to the OUV of the property.



Integration into local, regional and national planning systems (including sea/landscape connectivity)
Some Concern
BMNP is integrated into local, national, and regional planning systems through mechanisms outlined in its General Management Plan (GMP) 2017-2027. The park's management approach aligns with national environmental governance frameworks, requiring that development projects undergo Environmental Impact Assessments (EIA) to mitigate potential threats to its Outstanding Universal Value (OUV). Also an Integrated Environmental Management (IEM) system is part of the GMP ecosystem based approach.
While significant progress has been made at the national level, integration at the local level remains slow due to the failure to accord the park’s OUV the highest level of protection in planning processes (see threats explained above).
The GMP adopts an ecosystem-based approach that integrates participatory rangeland management. An Outreach Strategy further reinforces this integration by facilitating the exchange of information, education opportunities, and development initiatives that benefit both conservation and local communities.
However, on-the-ground limited prioritization of BMNP’s OUV in local decision-making processes limits and undermines the effectiveness of BMNP conservation strategies.
Boundaries
Some Concern
The boundaries of the site are well-defined and align with the designated area of the park, effectively capturing its key biodiversity and ecological values under UNESCO World Heritage criteria (vii) and (x). Encompassing crucial habitats necessary for species survival, the park's boundaries are sufficiently large to support ecosystem functions, ensuring the continuity of biological processes and maintaining viable populations of its species assemblages. The spatial configuration of the park plays a vital role in sustaining these ecological processes, thereby enhancing ecosystem resilience and mitigating external pressures. The size and structure of the boundaries are deemed adequate for effective conservation management.
The park’s boundaries are legally defined, clearly demarcated, and officially gazetted, which should strengthen its protection and facilitates efficient management.
Surrounding BMNP is a well-established buffer zone that varies in width from approximately 5 to 20 Kilometers, encompassing all 29 adjacent kebeles (IUCN, 2024). This buffer zone should serve as a crucial protective mechanism, mitigating external threats and providing a transitional area where conservation-compatible activities can be implemented.

However, in reality, the boundary of the BMNP has not served its purpose thus far. Human encroachment into the park resulting in the escalating threats from increasing human settlements, expanding agriculture, deforestation, overgrazing, poaching, and unsustainable resource use is evidence that the boundary is not properly protected by management or respected by the local people.
The first and highest priority action must be to safeguard the boundaries of the Property as work continues to deal with other issues that are inside and outside the park.
Overlapping international designations
Data Deficient
Not applicable
Implementation of World Heritage Committee decisions and recommendations
Some Concern
In Decision 45 COM 8B.27 the UNESCO World Heritage Committee raised two concerns regarding the management of BMNP. First, the Committee sought to understand how the State Party was addressing the threats to the park’s OUV through the appropriate implementation of the GMP, particularly concerning unsustainable practices such as overgrazing by livestock. Second, the Committee requested clarification on how the State Party was ensuring that any proposed relocation of people and communities from within the park “follows a rights-based approach, ensuring free, prior, and informed consent (FPIC) of the affected communities and adhering to international best practices and applicable norms and standards” (WHC, 2023).

To address the issue of over-grazing, the State Party has developed a Grazing Pressure Reduction Strategy as part of the General Management Plan that aims to gradually reduce grazing within the park through a participatory approach that engages local communities. A key element of this strategy is the formation of Community-Based Organizations (CBOs), which will work with the government to establish natural resource management agreements. These agreements are intended to regulate grazing practices and promote sustainable livestock management. The implementation of this strategy is being phased over time, allowing communities to transition to alternative grazing practices and livelihoods (State Party of Ethiopia, 2024).
Additionally, the State Party is strengthening conservation regulations and law enforcement to prevent illegal grazing and habitat encroachment. Efforts are also being made to enhance stakeholder engagement, build institutional capacity, and address governance challenges. However, despite these initiatives, the effectiveness of the grazing reduction strategy remains uncertain. Limited financial resources, weak institutional capacity, and overlapping legislative mandates continue to pose significant obstacles. Furthermore, there is no clearly defined timeline for the full implementation of the grazing reduction measures, as success depends on multiple factors, including community cooperation and long-term policy support.
Beyond overgrazing, other significant threats such as deforestation, poaching, and infrastructure development also jeopardize BMNP’s ecological integrity. The GMP includes conservation measures to tackle these challenges, but enforcement remains difficult due to resource constraints and governance limitations. There is still no sufficient evidence of sustained financial investment and institutional strengthening, besides the development of strategies.
On ensuring the application of a rights-based approach to the relocation of communities, the State Party has committed to ensuring that any proposed relocation follows a rights-based approach, in accordance with international human rights standards and best practices that align with legal frameworks such as the United Nations Declaration on the Rights of Indigenous Peoples (UNDRIP) and the World Bank’s Environmental and Social Standards (ESS 5, 7, and 10).
To guide the relocation process, the State Party has taken several key steps: (i) Two steering committees have been established to oversee and guide the development of a multi-sectoral Integrated Relocation Action Plan, (ii) A Free, Prior, and Informed Consent (FPIC) Protocol has been developed to ensure that affected communities have a voice in decision-making and that they fully understand the implications of relocation, (iii) A Community Engagement Plan has been developed to facilitate open dialogue and information-sharing with affected households, (iv) A Grievance Redress Mechanism (GRM) has been developed to address concerns and ensure transparency throughout the process, and (v) Socio-economic surveys are being conducted to assess community needs and identify relocation sites that provide viable livelihood opportunities (State Party of Ethiopia, 2024).

However, despite these efforts, the relocation process remains highly complex and unpredictable. Many of the affected communities have deep cultural, spiritual, and socio-economic ties to the park, making voluntary relocation very challenging to achieve. In addition, the success of the initiative will depend on multiple factors, including community willingness, financial availability, and governance capacity. Resistance to relocation should be expected, and those households that may be agreeable will need a lot of support to transition successfully.
Climate action
Mostly Effective
The GMP includes specific provisions to protect the site's OUV from the negative impacts of climate change (EWCA, 2017). Recognizing the park as an important climate change reference area, the plan acknowledges that with global warming accelerating, the climate records of the Bale Mountains will be crucial for understanding the long-term effects of climate change on Afroalpine ecosystems.
Currently climate-smart agriculture is being piloted and the introduction of new crop varieties are being promoted by NGO partners in collaboration with the Sinana Agriculture Research Centre. BMNP should encourage the expansion of such initiatives and assist agriculture offices and other partners in promoting new crop varieties and indeed new crops. EWCA will also support the promotion of improved horticultural crops in park-associated communities such as highland fruits (apple, pear) production.
Furthermore, the management plan prioritizes ecological restoration as a means of counteracting land degradation caused by increased human settlement, overgrazing, and deforestation. By restoring ecosystem health, the plan seeks to mitigate the impacts of climate change and maintain biodiversity integrity.
A system is in place to measure and monitor climate change effects on the park’s OUV. The management plan underscores the importance of scientific research, particularly on the impact of climate change on endemic species distribution and ecosystem functioning. One of its key priorities is to monitor the habitat and altitudinal shifts of bird species within BMNP, which serve as indicators of climate change. The park’s climate data will be essential in assessing how rising temperatures affect high-altitude ecosystems and biodiversity over time.
BMNP is also managed to support and maximize global climate action efforts, including adaptation, mitigation, communication, and innovation. Adaptation is promoted through maintaining ecosystem resilience, ensuring functional connectivity, and prioritizing ecological restoration to reduce climate vulnerabilities. While the plan does not explicitly outline climate mitigation strategies, its focus on forest conservation and habitat restoration indirectly contributes to carbon sequestration and climate regulation. Additionally, the designation of BMNP as a climate reference area fosters research and knowledge-sharing on climate change impacts in Afroalpine ecosystems. By integrating these climate action strategies, the management plan aligns with broader global efforts to address climate change challenges.
In summary, the BMNP General Management Plan (2017–2027) integrates climate resilience strategies by ensuring the long-term sustainability of its ecosystems, monitoring climate change effects, and implementing ecological restoration efforts.
However, like all other activities outlined in the GMP, the incorporation of climate action strategies in various programmes while ecosystems, including forests, are experiencing intense threats from farming communities, overgrazing and increased settlements, remains a promise to be kept.
Management plan and overall management system
Serious Concern
The site is managed under a structured General Management Plan (GMP) that covers the period from 2017 to 2027, which provides a strategic and operational framework for managing the park and its interactions with surrounding communities (EWCA, 2017). It is organized into five key management programmes: Park Operations, Tourism Management, Interim Settlement & Grazing Management, Outreach, and Ecological Management. Each programme follows a logical framework approach that groups related topics together, aligning them with the park’s management responsibilities. The plan outlines a long-term strategy with guiding principles, objectives, and general actions that serve as a roadmap for achieving conservation and management goals.
A key feature of the GMP is its adaptive management structure, which includes a three-year rolling action plan for each programme. These action plans provide detailed steps for achieving programme objectives within short-term cycles, allowing for periodic assessment and adjustments based on progress and emerging challenges. The idea behind this structure is to ensure that the park’s management remains dynamic, flexible, and responsive to changing priorities, ecological conditions, and socio-political contexts. Additionally, a separate Tourism Development Plan guides actions aimed at improving community benefits from tourism while managing visitor impacts on the park. Despite this well-organized framework, the implementation of the GMP has faced several significant challenges. One of the main issues is the delay in executing the three-year action plans. The park is still operating within the first three-year cycle (2017–2020), meaning that subsequent updates and reviews have not progressed as planned. This stagnation limits the plan’s effectiveness and its ability to adapt to new conservation and management realities.
Another challenge is the over-reliance on external partners, such as the Frankfurt Zoological Society, as well as local Community-Based Organizations (CBOs) and task forces. Many of these partners have been assigned critical responsibilities, yet they may lack the financial and technical capacity to fulfil their roles effectively. This gap in resources may lead to inconsistencies in implementing planned actions, further delaying progress.
The GMP also identifies key threats to the park, such as human encroachment, settlement expansion, livestock grazing, and resource extraction. While it outlines measures to address these issues, park management has struggled to find sustainable solutions that balance conservation goals with the rights and livelihoods of local communities. Efforts to mitigate threats may face resistance from local populations who depend on natural resources for their survival, creating tensions that complicate enforcement and policy implementation.
Local employment and community wellbeing are integral to the park’s management strategy, particularly under the Outreach and Ecological Management Programme. The Tourism Development Plan is intended to foster economic benefits for local communities through sustainable tourism initiatives. However, these efforts have been insufficiently implemented, largely due to resource constraints and a lack of capacity among local organizations. In many cases, community-based conservation responsibilities have been assigned without adequate support, making it difficult for local stakeholders to effectively participate in conservation initiatives. The impact of BMNP management on local communities remains mixed. While some efforts have been made to integrate conservation with community benefits, conflicts over land use and resource access persist, explaining widespread illegal activities in the park.
The State Party acknowledges the need to balance conservation integrity with local rights, but practical implementation of this balance remains a work in progress (State Party of Ethiopia, 2024). Without stronger engagement strategies and tangible benefits for communities, resistance to conservation measures is likely to continue.
These challenges, particularly the delay in rolling out of the three-year action plans to ensure that the management plan remains up to date and relevant, calls for better coordination, stronger leadership, and regular progress reviews. Second, resource mobilization needs to be enhanced to ensure that partners and CBOs have the financial and technical capacity to carry out their assigned responsibilities. In conclusion, while the Bale Mountains National Park has a well-structured and thoughtfully designed management plan, its implementation has been hindered by delays, resource constraints, and limited community engagement. Addressing these challenges requires stronger coordination, increased funding, adaptive management, and a more inclusive approach that ensures both conservation goals and community needs are met. In the prevailing circumstances, the GMP is unable to fulfil its role as an effective guide for the sustainable management of this UNESCO World Heritage site.
Law enforcement
Some Concern
The legal framework within the site is enforced through a series of well-designed measures aimed at upholding conservation regulations while ensuring compliance with sustainability and biodiversity protection goals. The park has adopted advanced monitoring tools such as the SMART (Spatial Monitoring and Reporting Tool) and EarthRanger data systems to enhance the ability to track ranger movements, detect infringements, and collect critical data on wildlife and habitat conditions. These technological advancements have the capacity to strengthen law enforcement efforts by improving patrolling efficiency and ensuring a more coordinated approach to conservation. To further enhance enforcement capacity, rangers have undergone specialized training in community relations and law enforcement skills, equipping them with the necessary expertise to engage with local communities while effectively carrying out their duties. Additionally, a new patrol roster system to maximize ranger efforts, ensure comprehensive coverage of vulnerable areas and a timely response to potential threats has been introduced to strengthened the effectiveness of enforcement activities (State Party of Ethiopia, 2024).
Collaboration with local law enforcement agencies has also been prioritized, with formal Memorandums of Understanding (MoUs) signed to foster joint efforts in protecting the OUV. The enforcement framework includes a structured permit system that ensures compliance with park regulations while recognizing the rights of indigenous peoples and local communities to access resources in designated areas, while implementing fees and fines for unsustainable resource use (State Party of Ethiopia, 2024).
Rangers receive training on the appropriate use of force and human rights protection, with a strong emphasis on upholding the dignity of individuals while carrying out conservation responsibilities. A Grievance Redress Mechanism (GRM) has also been established as a platform for individuals and communities to voice concerns or file complaints.
These are steps in the right direction. However, protection of the OUV of the park will will require more enhanced efforts to effectively address the growing human population within the park and the corresponding high demand this population places on the resources found in the park. Effective law enforcement is needed to address illegal encroachment by permanent and temporary settlements, agricultural expansion, livestock grazing, deforestation as well as some unsustainable natural resource use (bamboo, honey, wild coffee harvesting and rangeland) inside the park. These will constitute the true measures of success.

Evidence of weak law enforcement include the admission in the BMNP of (i) increasing human settlement, (ii) increasing agricultural expansion, (iii) increasing grazing pressure, the three greatest threats to the OUV of the property. Over-harvesting of resources, particularly fuelwood and construction materials, has further degraded the park's ecosystems. All efforts to address these and other threats have not been significantly actualized on the ground, though many efforts have been made to develop programmes and mechanisms to implement them (see above).

Some of the weaknesses identified in the current management plan include (i) capacity - limited number of scouts, (ii) insufficient funds, (iii) poor patrolling system and practices, (iv) legally disempowered scouts and poor follow up on legal issues, (v) limited infrastructure for staff and patrolling over whole park; (vi) difficult access to remote areas, (vii) insufficient rapid back up for scouts from HQ (ECWA, 2017).
Sustainable finance
Serious Concern
An assessment of the financial resource needs has been reported in the GMP 2017-2027 (EWCA, 2017). The assessment observed that funding for the park has been inadequate for decades, making it difficult to implement effective management measures. The GMP reports that the park’s budget is among the lowest globally, at $0.8 per hectare, compared to a global average of $12.6 per hectare and regional averages of $9.7 per hectare in Tanzania and $10.0 per hectare in Kenya. This substantial funding gap presents a major challenge to maintaining the park’s ecological and cultural values. According to the GMP, the park relies on multiple funding sources, including carbon credits from REDD+, revenue from the Bale Mountains Eco-lodge in Harenna Forest, park entry fees, corporate and individual sponsorships, grants and donations, government central budget allocations, and a community conservation levy on park entrance fees (EWCA, 2017). However, many of these sources are unreliable. The GMP reports that several of these strategies have not yet yielded funds, while others face significant challenges due to bureaucratic hurdles, slow approval processes, and regulatory constraints. One major obstacle is that all revenue generated by BMNP is returned to the central treasury, leaving little flexibility for park managers to reinvest in operations. Additionally, any financial measures, such as fee adjustment or establishing trust funds, require approval from the Ethiopian Wildlife Conservation Authority (EWCA) headquarters or federal authorities, limiting the park’s ability to independently secure and manage its funds.
To address these financial constraints, BMNP has adopted a combination of cost-cutting and revenue-generating strategies through the privatization of Dinsho Lodge to reduce operational costs, and focuses on promoting research partnerships with academic institutions and increasing the use of volunteers to support park activities. Additionally, Ethiopian government is expected to increase financial support, particularly for significant expenses such as the relocation compensation for park inhabitants..
Despite these efforts, financial sustainability remains a major concern for BMNP. Structural changes are needed to allow the park to retain at least a substantial portion of its revenue, and some flexibility in diversifying funding sources.
Staff capacity, training and development
Some Concern
The site faces significant challenges in staff capacity, training, and development, which are crucial for effective in the management of the property. The current GMP acknowledges these shortfalls and outlines actions to address them (EWCA, 2017).
Staff capacity and numbers are currently insufficient to manage the park effectively. The number of scouts is inadequate, and overall working conditions, staff morale, and professionalism are not yet at the required level. Additionally, there are structural and staffing gaps, particularly in higher-level technical expertise, which affect the park’s ability to retain staff and address turnover issues.
Regarding staff capability and training, the GMP recognizes the need to build a professional and well-trained workforce. In 2015, park staff identified significant gaps in park management and administration, including poor salary packages, inadequate field and office equipment, and a lack of a computerized data management system. Well being, respect, and nurturing of staff by the management authority were aspects that were identified as requiring significant improvement. Poor and insufficient staff accommodation, a lack of employment benefits, and limited accident and medical insurance provisions are some of the areas flagged as requiring attention.
To address these concerns, the GMP proposes measures such as improving housing, providing uniforms, and introducing medical/accident insurance, and further recommends the acquisition of a transparent and effective human resource management system, along with an internal reward system to boost morale. It is not clear the extent to which these recommendations have been implemented.
The availability and accessibility of equipment and infrastructure are also areas of concern. Limited office and field equipment, as well as inadequate storage facilities hinder staff efficiency. Proper infrastructure, such as accommodation and workspaces, remains insufficient, which affects both morale and operational effectiveness .
Poor coordination at the management level exacerbates the problem, leading to inefficiencies in the upkeep and replacement of essential assets. While the GMP outlines steps to address these concerns, such as developing a strategy to fill capacity gaps and ensuring better human resource management, the extent to which these measures have been implemented remains to be evaluated.
Ultimately, the successful implementation of the GMP depends on the empowerment and motivation of BMNP staff. Ensuring that they are well-equipped, trained, and supported will be critical for achieving the park’s long-term conservation goals. Addressing these challenges will not only improve staff capacity but also enhance the overall management effectiveness of the site.
Education and interpretation programmes
Mostly Effective
Education, interpretation, and awareness programs play a crucial role in enhancing the understanding of Bale Mountains National Park’s (BMNP) values among various stakeholders, including local communities and government bodies. Through environmental education initiatives, the park has developed strategies to create awareness about its ecological significance and promotes responsible behaviour towards conservation. These programmes are designed to not only provide information about BMNP’s importance as a UNESCO World Heritage site but also to inspire action and behavioural change among stakeholders. By integrating environmental education into both formal and informal settings, these efforts help bridge the gap between conservation principles and local realities, reinforcing cultural and traditional knowledge while advocating for sustainable interactions with the park. The involvement of organizations such as the Ethiopian Wolf Conservation Programme, Melca Mahiber, FZS, and Farm Africa/SOS Sahel has further strengthened these programmes by offering targeted education for park-adjacent communities.
In terms of regulations and sustainable resource use, the park has created education and awareness programmes to ensure that communities and stakeholders understand the importance of adhering to conservation guidelines. These efforts aim to explain the rationale behind BMNP’s existence, emphasizing the need for sustainable management of its resources. The management plan outlines key actions to enhance conservation education, such as developing a comprehensive environmental education strategy, evaluating and harmonizing existing programs, and identifying target audiences with clear, outcome-based messaging. Additionally, the capacity of park and government staff is being strengthened to improve environmental education delivery. Programs targeting schools and elders' environmental clubs have been expanded, and include visits to the park for key stakeholders to deepen their understanding of conservation challenges. These initiatives are collectively aimed at contributing to an informed stakeholder base that supports the park’s long-term sustainability while fostering community involvement in resource management.
Tourism and visitation management
Some Concern
The Ethiopian government, along with conservation organizations, recognizes BMNP as a critical natural and cultural asset, incorporating its values into broader tourism strategies. These policies emphasize the park’s role in sustainable tourism, highlighting its endemic species such as the Ethiopian wolf and mountain nyala, as well as its breathtaking landscapes, including the Sanetti Plateau and Harenna Forest. The inclusion of BMNP in national tourism planning ensures that its ecological and cultural importance is actively promoted both domestically and internationally.
The BMNP General Management Plan (GMP) for 2017–2027 provides a well-defined tourism and visitation framework aimed at enhancing visitor experiences while preserving the park’s ecological integrity. The GMP outlines a structured approach to managing visitor services, ensuring that tourism development aligns with conservation goals. The plan recognizes the need for regulated tourism growth, balancing increased visitation with the protection of BMNP’s unique biodiversity.
Overall, BMNP’s tourism strategy, as outlined in the GMP, seeks to balance visitor experiences with conservation priorities. The plan recognizes the park’s potential to becoming a leading ecotourism destination in Africa while ensuring that tourism development remains environmentally and socially responsible. Through sustainable infrastructure, community involvement, and stringent impact management, BMNP is positioned to enhance its global appeal while preserving its extraordinary natural and cultural heritage.
However, the message from the GMP is sobering: It reads, “(i) The presence of human settlements and domestic livestock in many areas of the BMNP has a highly detrimental effect on tourism prospects. This is not normal in national parks around the world and if Ethiopia has ambitions to compete internationally as a tourism destination this issue must be urgently addressed; (ii) Overgrazing by livestock results in a lack of botanical diversity, insect life and consequently the presence of birds and other charismatic wildlife; (iii) Human presence serves to disturb wildlife (making it more difficult for visitors to experience wildlife viewing) and erodes the natural/wilderness character of the Park; (iv) Perhaps the most significant issue of all is the prospect of rabies transmission from domestic dogs to Ethiopian wolves – a major threat to the BMNP’s best tourism asset. In general, visitors are always happy to encounter local people and are interested to learn about and experience local culture and customs, (v) The presence of the public road within the BMNP makes non-tourism traffic noise and visibility a significant issue in certain locations”.
It is notable the OUV and tourism in BMNP are threatened by exactly the same factors. It is, therefore, reasonable that they share the same concerns.
Sustainable use
Serious Concern
The General Management Plan (2017–2027) outlines a structured approach to ensuring the sustainable use of natural resources while maintaining the conservation values of the park. The plan integrates conservation priorities with community livelihoods, aiming to balance ecological integrity with sustainable resource utilization.
Assessments of the type and level of resources that can be extracted without jeopardizing the park’s conservation status have been identified as a critical area of focus. The management plan emphasizes the need for research to determine sustainable extraction limits and assess the impact of legal resource harvesting (EWCA, 2017).
To ensure that resource use within and around BMNP remains sustainable and does not negatively impact its conservation values, several mechanisms have been established. The management plan encourages regulated agreements for seasonal resource use, ensuring that practices such as beekeeping and honey harvesting follow sustainable guidelines. Additionally, the Participatory Forest Management (PFM) model has been instrumental in engaging communities in conservation efforts, fostering a sense of shared responsibility (State Party of Ethiopia, 2024). The plan also highlights the importance of collaboration among government agencies, conservation authorities, and local communities in managing the controlled hunting areas (CHAs) and refining quota systems for species like the mountain nyala. However, there are still gaps in enforcement, monitoring, and benefit-sharing mechanisms, which require further strengthening to achieve long-term sustainability.
Despite the efforts to regulate resource use, some activities currently pose threats to the conservation of BMNP. The expansion of semi-forest and forest coffee production, while economically significant, presents a risk of biodiversity loss if not properly managed. Similarly, unsustainable harvesting of non-timber resources such as bamboo and grass is an ecological concern. The plan acknowledges these threats and proposes solutions such as promoting alternative livelihoods, encouraging sustainable agricultural practices, and implementing stricter monitoring of resource extraction. Strengthening enforcement mechanisms, increasing community involvement in decision-making, and providing incentives for conservation-friendly practices are critical steps to mitigating these threats.
The plan also recognizes the rights of local communities to access cultural and natural resources within BMNP. Community members are allowed to engage in regulated resource use activities, including beekeeping, honey harvesting, and forage collection, through structured agreements. However, challenges remain, particularly in the governance of controlled hunting areas, where local communities have had limited participation and benefit-sharing opportunities (Gulte et al. 2023). The plan seeks to enhance community involvement in CHA governance to ensure that economic benefits are more equitably distributed and that local people develop a stronger stake in conservation efforts. The success of Participatory Forest Management provides a model that could be expanded to other resource governance areas, reinforcing the rights of rightsholders while maintaining ecological sustainability.
In conclusion, BMNP’s General Management Plan demonstrates a commitment to balancing conservation and sustainable use. While assessments of resource use sustainability are ongoing, and mechanisms have been put in place to regulate resource extraction, though some gaps in enforcement and benefit-sharing remain. Unsustainable practices, particularly in coffee expansion and non-timber resource harvesting, pose risks that require stronger regulatory frameworks and alternative livelihood strategies.
Monitoring
Some Concern
BMNP GMP has a structured Monitoring and Evaluation (M&E) framework to track conservation status and assess management effectiveness (EWCA, 2017). This includes social, economic, and environmental monitoring programs, with the Ecological and Threat Monitoring (ETM) Programme playing a key role in tracking wildlife populations and environmental pressures. Regular monitoring is conducted by the Ethiopian Wildlife Conservation Authority (EWCA), park management, and conservation partners like the Frankfurt Zoological Society (FZS) and the Ethiopian Wolf Conservation Programme (EWCP). The EU-funded SHARE II Project assesses socio-economic impacts, ensuring that conservation benefits, such as tourism and livelihoods, are also monitored.
However, BMNP faces significant challenges. Limited financial and human resources constrain monitoring efforts, with heavy reliance on external funding. Community participation in ecological monitoring remains weak, missing opportunities to integrate traditional knowledge. Inconsistent funding has led to gaps in long-term ecological data, and weak stakeholder coordination reduces efficiency in data collection and analysis. Moreover, climate change monitoring is inadequate, limiting adaptation strategies, and enforcement against illegal activities like poaching and overgrazing is weak. Over-reliance on external expertise also hinders the development of local research capacity.
Limited implementation of the monitoring programme undermines the ability of the park to effectively use the adaptive management approach to conserve BMNP resources and protect its World Heritage values.
Research
Mostly Effective
Research in BMNP is carried out to support adaptive management and conservation planning. A prioritized research list provided in the GMP aims to align research with conservation priorities. The list also serves as a guide for future studies, promoting studies to address knowledge gaps (EWCA, 2017). Due to resource limitations, BMNP relies on partnerships with academic and research institutions to enhance data collection and conservation decision-making.
BMNP management facilitates research by assisting with permits, providing logistical support, and helping secure funding. Operational guidelines ensure data sharing and capacity building, though further efforts are needed to maintain a centralized research database.
Strengthening institutional capacity, inhouse funding for critical research on priority management needs, improved collaborations and partnerships will remain key to maintaining BMNP’s ecological integrity and long-term conservation success. However, a mechanisms for evaluating and implementing critical research findings should be established .
Effectiveness of management system and governance in addressing threats outside the site
Some Concern
The information provided in this assessment indicates that the management system is unable to address threats outside the BMNP. It has not managed to stop the encroachment of people entering the park from the 26 Kebeles that surround it (EWCA, 2017) and use BMNP as alternative communal grazing areas. The GMP indicates that most outreach programmes working on activities outside BMNP do not fall under BMNP mandate, and are mainly donor funded. However, through the GMP outreach programme strategy, BMNP will facilitate such projects to ensure that activities are in line with park development and reduced pressure on the park. This raises serious concerns because the escalating threats to BMNP (i.e., human encroachment with their livestock and increasing demand for agricultural land and other ecosystem services and resources) are originating from outside the park. The GMP reports that public land administration authorities in the areas surrounding the park do not have the capacity or funds to develop legally binding land use plans and also lack regulatory capacity for their implementation.
Effectiveness of management system and governance in addressing threats inside the site
Serious Concern
The 2017-2027 ten year General Management Plan is still in the first phase of implementation. Most of the activities have been focused on developing strategies, programmes and tools for implementing action on the ground (such as signing Park Cooperative Agreements, developing Core Protection Zones, establishing steering committees to guide the relocation, developing a socio-economic survey tool, establishing a Community Engagement Plan and Free, Prior, and Informed Consent Protocol, establishing a Grievance Redress Mechanism, developing the Grazing Management Plan, instituting a system of fees and fines associated with resource use, implementing a new patrol rosters system, equipping ranger teams with the necessary gear and technology, signing MoU with local law enforcement agencies, conducting training sessions for rangers focused on human rights and the appropriate use of force (see State Party of Ethiopia, 2024). Although all these efforts are critical for achieving the overall conservation objectives, they are inadequate to addressing the significant threats facing the OUV of the property. The GMP’s strategic vision is sound, but implementation gaps and structural barriers currently prevent meaningful threat reduction.
The assessment of BMNP’s management system and governance reveals inadequacies in protecting its OUV. While the General Management Plan (GMP) 2017-2027 outlines critical strategies, its implementation remains in its early stages, despite escalating threats to the site. Key challenges, including agricultural expansion, settlements, overgrazing, and unsustainable resource harvesting, persist with little on-the-ground mitigation. The planned relocation of communities remains in the planning phase, further highlighting delays in execution and raising concerns regarding the just and equitable engagement of local communities. Failure to effectively protect the boundaries is undermining the OUV, casting doubts on the effectiveness of other programmes. Furthermore, management effectiveness cannot yet be properly evaluated, as many strategies remain either unimplemented or in the planning stages. The current plan is significantly behind schedule, still in its first cycle (2017-2020) while it should be in its final phase (2024-2027). Limited funding, inadequate staffing, and the complexities of relationships with local communities are key barriers to progress. The delay in taking decisive actions, particularly providing sufficient funding to place the World Heritage site on a sound footing, coupled with uncertainties in the timelines for the implementation of critical threat-abating strategies makes it difficult to establish realistic periods for delivering the various expected outcomes. In summary, most of the elements of a good plan are in place, however the key barrier to effective management is the implementation. High impact interventions can and should be carried out in the short-term to safeguard the ecological integrity of the site, including securing the boundaries to prevent further encroachment and illegal activities. However, without immediate, sustained, and well-supported interventions, the OUV of the site will continue to be degraded.
Good practice examples
The General Management Plan (GMP) 2017-2027 for Bale Mountains National Park (BMNP) stands as a well-structured and forward-thinking framework designed to balance biodiversity conservation, sustainable resource management, and community engagement. It provides a strong legal foundation, aligning with national and international conservation policies, including IUCN standards and UNESCO World Heritage requirements. Through zoning regulations and Core Protection Zones (CPZs), it ensures ecological sustainability while integrating conservation with local development strategies. A major strength of the GMP is its commitment to community participation and rights-based governance. It establishes Free, Prior, and Informed Consent (FPIC) mechanisms, Grievance Redress Mechanisms (GRM), and Participatory Forest Management Associations (PFMAs), allowing local communities to play an active role in park management. Additionally, it promotes alternative livelihoods and ecotourism, offering economic incentives for conservation. The plan also takes a scientific and adaptive management approach, integrating a Monitoring and Evaluation (M&E) framework to assess conservation progress. Technological advancements, such as SMART and EarthRanger monitoring systems, enhance law enforcement and biodiversity tracking. Recognizing BMNP as a key climate change reference area, the GMP supports climate resilience strategies, ecological restoration, and sustainable agriculture. Furthermore, the GMP’s Tourism Development Plan strategically positions BMNP as a premier ecotourism destination, ensuring visitor experiences are well-managed while minimizing environmental impact. Institutional collaborations with organizations like Frankfurt Zoological Society (FZS) and the Ethiopian Wolf Conservation Programme (EWCP) further strengthen conservation efforts. In essence, the GMP is a comprehensive and visionary framework that fosters biodiversity protection, climate resilience, sustainable tourism, and community empowerment. It lays the groundwork for BMNP’s long-term sustainability, ensuring that conservation objectives align with socio-economic development for the benefit of both nature and people.

Landscape mosaic of extraordinary beauty

High Concern
Trend
Stable
A display of an immense variety of landscapes that captivate the senses from an ever-changing spectacle of nature’s grandeur demonstrated high volcanic peaks and ridges, dramatic escarpments, sweeping valleys, glacial lakes, deep gorges and spectacular waterfalls is being distracted by the changing vegetation composition and structure occasioned by human activities, including agriculture, grazing, settlements, effects of fires, wood extraction, quarrying, and some infrastructure.

Steep altitudinal gradient that sculpts the land and vegetation

High Concern
Trend
Deteriorating
The natural beauty displayed by changing layers of vegetation types in dramatic succession along the park’s steep altitudinal gradient from the lowland woodlands to the Afroalpine peaks that give the the park an unparalleled sense of grander and ecological richness is interrupted by sights of farmlands, overgrazed landscapes and unplanned settlements in nearly all areas of the park. Threats that are rated high and increasing include agriculture and settlements in Harena; fire, wood extraction, settlements, livestock in Erica; Settlements, agriculture and livestock in Hagenia, and livestock and settlement in the Alpine region. Other threats rated as moderate but increasing include wood extraction and grazing in Harena; wood extraction in Hagenia and wood extraction, infrastructure and agriculture in the Alpine region (EWCA, 2017).

Breathtaking hydrological features and sceneries

High Concern
Trend
Stable
The breathtaking hydrological features and sceneries created by numerous glacial lakes, lush wetlands, dramatic waterfalls and seasonal flooded Afroalpine bogs are impacted mainly by livestock grazing and agricultural activities which are rated high and settlements that is rated moderate and grass cutting. According to the GMP (EWCA, 2017), these threats are increasing.

A geological and glaciological marvel

Good
Trend
Stable
The geological and glaciological marvel remains in good condition.

Distinct ecosystems and high habitat diversity of outstanding importance for in-situ conservation of a diverse assemblage of species

High Concern
Trend
Deteriorating
The distinct ecological zones and vegetation from lowland grasslands to Afroalpine moorlands that support a unique assemblage of species, many of which are endemic and adapted to the park’s altitudinal diversity, including large herbivores such as bushbucks, warthogs, and Bohor reedbuck in Lowland Grasslands and Woodlands, the rare and endemic species such as the Bale monkey (Chlorocebus djamdjamensis) and Menelik’s bushbuck in the Harenna Forest; the endemic and endangered Ethiopian wolf (Canis simensis) in the Erica Belt and highly specialized flora, including the giant lobelia (Lobelia rhynchopetalum) and 80% of the endemic species in the Afroalpine Moorlands face the threat from agriculture, settlements, livestock, fire, wood extraction, and poaching, among others. Threats to these ecosystems that are rated high and increasing include agriculture and settlements in Harena; fire, wood extraction, settlements, livestock in Erica; Settlements, agriculture and livestock in Hagenia; and livestock and settlement in the Alpine region. Other threats rated as moderate but increasing include wood extraction and grazing in Harena; wood extraction in Hagenia and wood extraction, infrastructure and agriculture in the Alpine region. The Ethiopian wolf faces severe threat from rabies and canine distemper that are transmitted by domestic dogs (EWCA, 2017).

High degree of floral species richness and endemism

High Concern
Trend
Deteriorating
Human activities are significantly impacting on the critical habitats for in-situ conservation for many faunal and floral species in BMNP, including 1,660 documented species of flowering plants, most important site for genetic stocks of the wild variety of a major coffee species (Coffea arabica). The varied altitudinal gradients and microclimates within the park provide suitable habitats for high species diversity of bryophytes, including mosses and liverworts, and rich community of fungi, including mycorrhizal species. There are 337 plant species of medicinal plants. Threats to these habitats have generally been on the increase. Those that are rated high and increasing include agriculture and settlements in Harena; fire, wood extraction, settlements, livestock in Erica; Settlements, agriculture and livestock in Hagenia; and livestock and settlement in the Alpine region. Other threats rated as moderate but increasing include wood extraction and grazing in Harena; wood extraction in Hagenia and wood extraction, infrastructure and agriculture in the Alpine region. These critical habitats are also facing threats from unsustainable harvesting of non-timber NR, e.g. bamboo, grass, coffee, particularly in Harena forest, and invasive species in Harena and Erica zones. Climate change is also likely to disrupt and alter the current spatial arrangement, diversity, and distribution of
many endemic and non-endemic species of the afroalpine range. In the Bale Mountains, both the upper and lower margins of distributions of Erica are highly likely to be affected. Kidane et al. (2022) modelled Erica’s future habitat such as the area of habitat gain (expansion)—western, northern, and eastern fanks of the massif and afroalpine top; persistence and dominance—most of the midaltitude and its current range; and loss (reduction/ contraction)—most of the lower ranges of current distribution. However, Erica’s future expansion will lead to considerable species replacement, local extinction, and a significant decrease in the species richness of those endemics on the afroalpine plateau. Hence, ecosystems of the afroalpine plateaus and associated unique flora and fauna are highly threatened by climate change.

High degree of faunal species richness and endemism

High Concern
Trend
Deteriorating
According to the State Party, monitoring has shown that the Ethiopian wolf population has stabilized over the past four years, following significant mortality events linked to rabies and canine distemper. This positive trend is largely attributable to ongoing vaccination efforts, which include comprehensive initiatives such as oral rabies vaccinations for wolf packs throughout the Bale Mountains, as well as a targeted canine distemper vaccination trial undertaken with select packs (State Party of Ethiopia, 2024). Nevertheless, with limited testing on these measures (as mentioned in the threats section) it is important to continue monitoring the potential negative impacts too. Recent surveys indicate that the Mountain Nyala is expanding its habitat range, with small groups increasingly observed outside their previously established core areas. These observations suggest that the overall population of the Mountain Nyala has remained stable over the past five years (State Party of Ethiopia, 2024). In regards to the Bale monkey (Chlorocebus djamdjamensis), the range of this species is less than 20,000 km² with severe fragmentation and there is continuing decline due to ongoing habitat loss and degradation. Habitat destruction, agricultural land expansion, and human settlement are major threats of the species, which are showing a declining trend (Worku, 2019).

With ongoing discoveries of new species, BMNP remains a globally significant biodiversity hotspot. However, threats from human activities are likely to rob the world of many of the endemic species. The threats that are rated high and increasing include agriculture and settlements in Harena, where for example shrew species (Crocidura harenna, Cercopithecus djamdjamensis, and Mus triton) and Bale Monkey are endemics restricted to this (Lavrenchenko et al. 2017). Other high threats are fire, wood extraction, settlements, livestock in Erica which hosts endemic and threatened tree species including Erica arborea and E. trimera; endemic amphibians and reptiles including Balebreviceps spp and Ericabatrachus spp; endemic rodent spp including Megadendromus nikolausi; endemic and near endemic bird species Rouget’s rail (Rougetti rougetti) and Bale parisoma (Parisoma greaventris). High threats in Hagennia are settlements, agriculture and livestock which is home to the endemic rodents White-footed rat (Praomysalbipes). Within the Alpine region, threats rated high include livestock and settlement. This region hosts seven endemic species.

Viable populations of rare and globally threatened species of outstanding universal value

High Concern
Trend
Deteriorating
BMNP is vitally important for 13 globally rare and threatened mammal species that are vulnerable (VU), endangered (EN) or critically endangered (CR), according to the IUCN Red List. Besides flagship species such as Ethiopian wolf, mountain nyala and Bale monkey, BMNP also hosts isolated and threatened populations of the endangered wild dog (Lycaon pictus) and the vulnerable black maned lion (Panthera leo) (Datson 2002; OARBD 2007). The park is home for at least 29 globally threatened or endangered bird species (Redman et al. 2011 and IUCN, 2020). As per this date, nine bird species are vulnerable (VU), twelve near threatened (NT), four are endangered (EN) and another four critically endangered (CR). The site also supports the migration of over 170 migratory bird species, such as wintering and passing raptors, including the Greater Spotted Eagle (indicating park's role in avian migration routes) (BMNP 2021). These species occur in all the habits within the park, and are being affected by the many and increasing threats. The threats that are rated high and increasing include agriculture and settlements in Harena; fire, wood extraction, settlements, livestock in Erica; Settlements, agriculture and livestock in Hagenia; and livestock and settlement in the Alpine region. Other threats rated as moderate but increasing include wood extraction and grazing in Harena; wood extraction in Hagenia and wood extraction, infrastructure and agriculture in the Alpine region. These critical habitats are also facing threats from unsustainable harvesting of non-timber NR, e.g. bamboo, grass, coffee, particularly in Harena forest, and invasive species in Harena and Erica zones.
Assessment of the current state and trend of World Heritage values
Deteriorating
With the continued increase of previously identified threats, most key attributes are of high concern and deteriorating. The property boundaries have remained porous, and human activities have escalated. Until these issues are addressed, the state of conservation is likely to deteriorate. Habitat fragmentation and loss due to human activities is affecting overall flora and fauna species richness. Ecosystems of the afroalpine plateaus and associated unique flora and fauna are also highly threatened by climate change. Although there are indications that the Ethiopian wolf and Mountain nyala populations in the property have stabilised over the past 4-5 years, agricultural and settlement expansion remain major threats. The range of the Bale monkey is decreasing rapidly due to ongoing habitat fragmentation and this is likely affecting a range of species, especially those associated with specific habitats.
Assessment of the current state and trend of other important biodiversity values
High Concern
Data Deficient
Other important biodiversity values include (i) Critical genetic reservoir for Wild Forest Coffee, (Coffea arabica), BMNP being one of the only two sites in the world where a naturally occurring wild population continues to be viable. (ii)The site is of great medicinal value, being a source of 337 medicinal plant species which comprise approximately 40% of all Ethiopian medicinal plant species, 24 of which are endemic (National Herbarium, 2004; Lulekal, 2005; Yineger, 2005). (iii) Significant Hydrological Significance: The park is the source of numerous major rivers, including the Web, Wabe Shebele, Welmel, Dumal, and Ganale, which support the livelihoods of millions of people within and beyond Ethiopia. These values are affected by human activities - agriculture and settlements in Harena; fire, wood extraction, settlements, livestock in Erica; Settlements, agriculture and livestock in Hagenia; and livestock and settlement in the Alpine region. Other threats rated as moderate but increasing include wood extraction and grazing in Harena; wood extraction in Hagenia and wood extraction, infrastructure and agriculture in the Alpine region. Nevertheless, the trend of other bidoiversity values remains unclear.

Additional information

Provision of jobs,
Tourism-related income
According to data obtained from the Frankfurt Zoological Society of Ethiopia, the BMNP is also important in providing
economic benefits through eco-tourism activities such as control hunting and engagement
associations in different activities like tourist guides, horse renters, porters, cooks, handicrafts, coffee
providers, and honey providers. In line with this, about ETB 8,946,645.55 (equivalent to US$ 173,098
based on the exchange rate on 8 June 2022) has been generated from 2018 to 2021 through 26
community-based organizations engaged in control hunting activities organized in three control hunting
areas. Similarly, ecotourism association engaged in varies activities
generated ETB 5,917,696 from 2010 to 2021 (equivalent to US$ 114,494
based on exchange rate on 8 June 2022) (Gulte et al. 2022).
Collection of timber, e.g. fuelwood,
Sustainable extraction of materials (e.g. coral, shells, resin, rubber, grass, rattan, etc)
The most dominant perceived benefits among all items was fire wood and fodder which account 80%, followed by medicinal plant (67%), bee keeping (60%) (Koricha and Adem, 2024).
The BMNP is important in providing economic benefits through various eco-tourism activities and material benefits like fire wood, fodder, medicinal plants and many others. Especially for local communities the site is of critical importance.

References

References
1
Alers, M., Bovarnick, A., Boyle, T., Mackinnon, K., Sobrevila, C. (2007). Reducing threats to protected areas: Lessons from the field. A Joint UNDP and World Bank GEF Lessons Learned study. The International Bank for Reconstruction and Development and the United Nations Development Programme, USA,102 pp.
2
Anteneh, B. and Temesgen, Y. (2009). Extensive forest fire of 2007/2008 in the Bale Mountains National Park of southeast Ethiopia: extent, causes and consequences. In Ensermu Kelbessa and Abenet Girma (eds). Tackling the frequent forest fire incidence in Ethiopia. Proceding of a workshop. Occeasional report No. 2/2009. 47-76pp.
3
Anteneh, G., Melaku, B., and Teshale, W. (2014). Natural resource use conflicts in Bale Mountains National Park, Southeast Ethiopia. Int. J. Biodiver. Conser. 6(12):814-822
4
Asefa, A. (2006). Birds of Bale Mountains National Park, Southeast Ethiopia. Walia, 25: 22-33.
5
Asefa, A. (2008). Mountain Nyala and Ethiopian Wolf Mortalities in the northern side of Bale Mountains National Park, Ethiopia. Ethiopian Journal of Biological Sciences, 7(2): 179-184.
6
Asefa, A. (2011). Mammals of the Bale Mountains National Park, Ethiopia: A Compiled and Annotated Checklist. Walia-Special Edition on the Bale Mountains, 3-14.
7
Asefa, A., Richman, E., Admassu, B. & Baggallay, T. (2013). Bale Mountains National Park: Birding Booklet. The Ethiopian Wildlife Conservation Authority, Addis Ababa, Ethiopia.
8
Asefa, M., Cao, M., He, Y., Mekonnen, E., Song, X., & Yang, J. (2020). Ethiopian vegetation types, climate and topography. Plant diversity, 42(4), 302-311.
9
Atickem A., Loe, L.E., Langangen, Ø,. Rueness, E. K., Bekele, A. and Stenseth, N.C. (2010). Estimating population size and habitat suitability for mountain nyala in areas with different protection status. Animal Conservation 14 (2011) 409–418.
10
BMNP (2025). Challenges. Bale Mountains National Park. Available at: https://balemountains.org/challenges/
11
BMNP (2025). Current Challenges. Bale Mountains National Park, Ethiopia. Available at: https://balemountains.org/the-park/challenges/current-chall…
12
Belayneh, A., Yohannes, T., & Worku, A. (2013). Recurrent and extensive forest fire incidence in the Bale Mountains National Park (BMNP), Ethiopia: extent, cause and consequences. Int J Environ Sci, 2(1), 29-39.
13
Burgess, Neil, Jennifer D’Amico Hales, Emma Underwood (2004). Terrestrial Eco-region Eco-regions of Africa and Madagascar: A Conservation Assessment. Island Press, Washington DC, USA.
14
Carabassa, V., Domene, X., Díaz, E., Alcañiz, J.M. (2020). Mid-term Effects on Ecosystem Services of Quarry Restoration with Technosols under Mediterranean Conditions: 10-year Impacts on Soil Organic Carbon and Vegetation Development. Restor. Ecol. 28, 960–970.
15
Datson, G. (2002). Survey of African Wild Dogs in the Harenna Forest, Ethiopia. BirdLife International, Cambridge, UK.
16
EWCA (2017). Bale Mountains National Park General Management Plan (2017 – 2027). Ethiopian Wildlife Conservation Authority. Addis ababa, Ethiopia.
17
EWCA (2024). State of Conservation Report of Bale Mountains National Park World Heritage Site. Ethiopian Wildlife Conservation Authority. Addis Ababa, Ethiopia.
18
Endalew, A.,Tasew, E., Tolahun, S. (2019). Environment and Social Impacts of Stone Quarrying: South Western Ethiopia, in Case of Bahir Dar Zuria Wereda Zenzelma Kebele. Int. J. Res. Environ. Sci. 5, 29–38.
19
Farm Africa (2008). Bale Mountains Eco-Region Sustainable Development Plan Report on Phase I and II Planning Workshops in Goba, Bale 15-17 September 2008 (Phase I) and 25-26 November 2008 (Phase II), 29 pp.
20
Farm Africa and SOS Sahel Ethiopia (2014). Bale Mountains Eco-region Reduction of Emission from Deforestation and Forest Degradation (REDD+) Project- Ethiopia 145 pp.
21
Flintan, F., Chibsa, W., Wako, D., Ridgewell, R., (2008). Livestock and livestock systems in the Bale Mountains ecoregion: a report for the Bale ecoregion sustainable management project, SOS Sahel Ethiopia and FARM Africa. Addis Ababa, Ethiopia.
22
Gashaw T. (2015). Threats of Bale Mountains National Park and solutions, Ethiopia. Journal of Physical Science and Environmental Studies, 1(2), 10-16.
23
Gil-Romera, G., Adolf, C., Benito, B. M., Bittner, L., Johansson, M. U., Grady, D. A., ... & Miehe, G. (2019). Long-term fire resilience of the ericaceous belt, Bale Mountains, Ethiopia. Biology Letters, 15(7), 20190357.
24
Gippoliti S., Butynski T., Mekommen, A (2019). Chlorocebus djamdjamensis. The IUCN Red List of Threatened Species 2019. DOI: 10.2305/IUCN.UK.2019-3.RLTS.T4240A17958005.en
25
Gower, D. J., Wade, E. O., Spawls, S., Böhme, W. O. L. F. G. A. N. G., Buechley, E. R., Sykes, D., & Colston, T. J. (2016). A new large species of Bitis Gray, 1842 (Serpentes: Viperidae) from the Bale Mountains of Ethiopia. Zootaxa, 4093(1), 41-63.
26
Gulte, E., Tadele, H., Haileslassie, A., & Mekuria, W. (2023). Perception of local communities on protected areas: lessons drawn from the Bale Mountains National Park, Ethiopia. Ecosystems and People, 19(1), 2227282.
27
Gulte, E., Tadele, H., Haileslassie, A., & Mekuria, W. (2023). Perception of local communities on protected areas: lessons drawn from the Bale Mountains National Park, Ethiopia. Ecosystems and People, 19(1).
28
Hagmann, T., & Mulugeta, A. (2008). Pastoral Conflicts and State-Building in the Ethiopian Lowlands. Afrika Spectrum, 43(1), 19-37.
29
Haydon DT, Randall DA, Matthews L, Knobel DL, Tallents LA, Gravenor MB. (2006). Low-coverage vaccination strategies for the conservation of endangered species. Nature. 443:692–5
30
Haydon, DT, Laurenson, MK, Sillero Zubiri, Z. (2002). Integrating epidemiology into population viability analysis: managing the risk posed by rabies and canine distemper to the Ethiopian wolf. Conservation Biology.16:1372–85.
31
Hillman, J. C. (1988). The Bale mountains national park area, Southeast Ethiopia, and its management. Mountain Research and Development, 253-258.
32
Jacobs MJ, Schloeder CA (2001). Impacts of conflict on biodiversity and protected areas in Ethiopia. Biodiversity Support Program, Washington, D.C, USA.
33
Jilo, S. A., Kebada, E. M., Derse, G. T., Aredo, B. M., & Shuge, A. H. (2023). The Role of One Health Approach Research for the Conservation of Endemic Wild Animals and Mitigation of Future Public Health Threat in Bale Mountains National Park, Ethiopia. J Water Res, 1(2), 73-77.
34
Johansson, M. U., Senay, S. D., Creathorn, E., Kassa, H., & Hylander, K. (2019). Change in heathland fire sizes inside vs. outside the Bale Mountains National Park, Ethiopia, over 50 years of fire-exclusion policy: lessons for REDD+. Ecology & Society, 24(4).
35
Kelboro, G., & Stellmacher, T. (2012). Contestations Over a Common Resource: The Case of Bale Mountains National Park, Ethiopia. Society & Natural Resources, 25(8), 789-804.
36
Kidane, Y. (2022). Vegetation diversity and distribution along the Bale mountains Afroalpine hotspot of biodiversity in the face of a fast-changing world (Doctoral dissertation). University of Bayreuth. Available at: https://epub.uni-bayreuth.de/id/eprint/6510/1/Yohannes%20Ki…
37
Kidane, Y. O., Hoffmann, S., Jaeschke, A., Beloiu, M., & Beierkuhnlein, C. (2022). Ericaceous vegetation of the Bale Mountains of Ethiopia will prevail in the face of climate change. Scientific Reports, 12(1), 1858.
38
Koricha, H. G., & Jemal Adem, M. (2024). Investigated the role of community based approaches for biodiversity conservation and socio-economic development in Bale Mountains National Park, Southeast Ethiopia. Scientific Reports, 14(1), 12241.
39
Largen M. & Spawls S. (2010). American Museum of Natural History amphibian database. American Museum of Natural History. Available at: http://research.amnh.org/vz/herpetology/amphibia/
40
Largen M. & Spawls S. (2011). Amphibians and Reptiles Recorded from the Bale Mountains. Walia-Special Edition on the Bale Mountains, pp 89-91.
41
Lavrenchenko, L. A., & Bekele, A. (2017). Diversity and conservation of Ethiopian mammals: what have we learned in 30 years?. Ethiopian journal of biological sciences, 16, 1-20.
42
Lepage D. (2020). Avibase -The Bird Checklist of the World, Bale Mountains National Park. Available at: https://avibase.bsc-eoc.org/checklist.jsp?region=ETor03&lis…
43
Loader, S., Mengistu, A., Schwaller, S., Gower, D., Nagel, P., Getahun, A., ... & Kassahun, R. (2009, July). Are Ethiopian highlands changing? Amphibians as ecosystem indicators. In Mountain Forum Bulletin (Vol. 9, No. 2). ICIMOD.
44
Lulekal, E., Kelbesa, E., Bekele, T. Yirga, H. (2008). An ethnobotanical study of medicinal plants in ManaAngetuWereda, southeastern Ethiopia. Journal of Ethnobiology Ethnomedicine;4:1-10.
45
Mahmud, Abdulhakim & Telila, Habte & Kumsa, Lemessa. (2024). Assessment of the impact of woody species encroachment on plant species diversity and the livelihood of pastoralists in southeastern Ethiopia. African Journal of Range & Forage Science. 41. 1-14. 10.2989/10220119.2024.2324866.
46
Marino, J., Sillero-Zubiri, C. and Macdonald, D.W. (2006). Trends, dynamics and resilience of an Ethiopian wolf population. Animal Conservation, 9: 49-58
47
Mekonnen, A., Bekele, A., Fashing,P.J., Lernould,J., Atickem, A., and . Stenseth, N. (2012). Newly Discovered Bale Monkey Populations in Forest Fragments in Southern Ethiopia: Evidence of Crop Raiding, Hybridization with Grivets, and Other Conservation Threats. American Journal of Primatology 74:423–432
48
Mekonnen, A., Atickem, A., & Williams, S. (2020). The Impact of Human Activities on the Bale Mountains Ecosystem and Its Wildlife. Biological Conservation, 245, 108572.
49
Mekonnen, Addisu; Rueness, Eli K.; et al. (2018). "Population genetic structure and evolutionary history of Bale monkeys (Chlorocebus djamdjamensis) in the southern Ethiopian Highlands". BMC Evolutionary Biology. 18 (106): 06.
50
Miehe, G. and Miehe, S. (1994). Ericaceous forest and heath land in Bale Mountains of South Ethiopia, Ecology and Man‘s Impact. Traut Warnke Verlag, Hamburg, Germany.
51
Muhammed, A., & Elias, E. (2021). Class and landscape level habitat fragmentation analysis in the Bale mountains national park, southeastern Ethiopia. Heliyon, 7(7).
52
Muhammed, M. A., Hassen, A. M., Abera, T. A., Wraase, L., Ejigu, B. L., Hailu, B. T., ... & Zeuss, D. (2024). Long-Term Volumetric Change Estimation of Red Ash Quarry Sites in the Afro-Alpine Ecosystem of Bale Mountains National Park in Ethiopia. Remote Sensing, 16(7), 1226.
53
Mussa, M., Teka, H., & Aliye, A. (2018). Socio-economic and environmental impacts of invasive plant species in selected districts of Bale Zone, Southeast Ethiopia. African Journal of Agricultural Research, 13(14), 673-681.
54
NH. (2004). Biodiversity assessment of the Bale Mountains National Park and surrounding areas. The National Herbarium of Addis Ababa University, Addis Ababa, Ethiopia.
55
OARDB. (2007). Bale Mountains National Park General Management Plan. Oromia Agriculture and Rural Development Bureau, Oromia National Regional State, Ethiopia.
56
RRF (2022). Emergency wildfire management in Bale Mountains. Rapid Response Facility. Available at: https://www.rapid-response.org/emergency-wildfire-managemen…
57
Richman, E. and Admassu, B. (2013). The Ethiopian Wildlife Conservation Authority (EWCA). A traveler’s Guidebook of Bale Mountains National Park. Frankfurt Zoological Society and the Bale Mountains National Park.
58
Sebsibe, I. (2022). Humans-livestock predators conflict in the Central and Eastern Part of Bale Mountains National Park, Ethiopia. BMC Ecology and Evolution, 22(1), 113.
59
Sillero-Zubiri, C., & Marino, J. (2017). Ethiopian Wolves: Ecology and Conservation of an Endangered Carnivore. Cambridge University Press.
60
Tadesse, S. A., & Kotler, B. P. (2016). Impact of Land Use and Land Cover Changes on the Wildlife Population in Bale Mountains National Park, Ethiopia. Environmental Management, 58(5), 882-896.
61
Urugo, M. M., Worku, M., Tola, Y. B., & Gemede, H. F. (2025). Ethiopian coffee: Production systems, geographical origin traceability, and European Union Deforestation Regulation directive compliance. Journal of Agriculture and Food Research, 101695.
62
Vial F. (2010). Conservation science for common ground: developing the necessary tools to manage livestock grazing pressure in Bale Mountains National Park, Ethiopia. PhD Thesis. University of Glasgow, UK.
63
Williams, S. D., Vivero, J. L., Spawls, S., Shimelis, A. & Kelbessa, E. (2005). Ethiopian Highlands. In: Mittermeier, R. (ed) Hotspots revisited. Conservation International and Cemex.
64
Worku, Z. (2019). The Endemic Bale Monkey (Chlorocebus djamdjamensis): Distribution and Threat, A Review Paper. Journal of Biology, Agriculture and Healthcare Vol.9, No.2, 2019.
65
Yimer, S (2023). World Heritage Site listing for Ethiopian park leads to eviction of farming community. Mongabay Africa. Published online 30 Oct 2023. Available at: https://news.mongabay.com/2023/10/world-heritage-site-listi…
66
Yimer, S (2023). World Heritage Site listing for Ethiopian park leads to eviction of farming community. Mongabay. Published 30 October 2023. Available at: https://news.mongabay.com/2023/10/world-heritage-site-listi…
67
Yineger,H., Kelbessa, E., Bekele, T. and Lulekal, E. (2008). Plants used in traditional management of human ailments at Bale Mountains National Park, Southeastern Ethiopia. Journal of Medicinal Plants Research Vol. 2(6), pp. 132-153.
68
Zewdie, B., Bawin, Y., Tack, A. J., Nemomissa, S., Tesfaye, K., Janssens, S. B., ... & Hylander, K. (2023). Genetic composition and diversity of Arabica coffee in the crop’s centre of origin and its impact on four major fungal diseases. Molecular Ecology, 32(10), 2484-2503.

Indigenous Heritage values

Would you like to share feedback to support the accuracy of information for this site? If so, send your comments below.

CAPTCHA
This question is for testing whether or not you are a human visitor and to prevent automated spam submissions.