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= Summary =  <!-- An overview of the site, with a one sentence overview of each of the following sections. can include a site map -->
 
= Summary =  <!-- An overview of the site, with a one sentence overview of each of the following sections. can include a site map -->
 
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<div style="float: right">
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{{#display_map: height=200px | width=300px | scrollzoom=off | zoom=5 | layers= OpenStreetMap, OpenTopoMap
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|9.20, -11.12~[[Loma Mountains National Park]]~Western Chimpanzee
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* Western chimpanzees (''Pan troglodytes verus'') are present in Loma Mountains National Park.  
 
* Western chimpanzees (''Pan troglodytes verus'') are present in Loma Mountains National Park.  
* It has been estimated that 1,065 (CI: 572-1,986) individuals occur at the site.  
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* It has been estimated that 1,390 (CI: 819-2,361) individuals occur at the site.  
* The chimpanzee population trend is unknown.  
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* The chimpanzee population trend is increasing.  
* This site has a total size of 332 km².  
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* This site has a total size of 288.5 km².  
* Key threats to chimpanzees are hunting and habitat encroachment due to farming.  
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* Key threats to chimpanzees are hunting, habitat encroachment due to farming, and fires.  
* Sierra Leone’s Forestry Division is responsible for the management and protection of the site; more information on conservation activities is lacking.
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* Conservation activities include environmental education, anti-poaching patrols, and reforestation.
* The status of the site was upgraded from non-hunting forest reserve to national park as part of a biodiversity offset for the Bumbuna hydroelectric dam.  
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* The status of the site was upgraded from non-hunting forest reserve to national park as part of a biodiversity offset for the Bumbuna hydroelectric dam.
    
= Site characteristics = <!-- A paragraph summary of physical and geographic aspects of the site, and a table of key information -->
 
= Site characteristics = <!-- A paragraph summary of physical and geographic aspects of the site, and a table of key information -->
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The site was first established as a non-hunting reserve in 1972, and upgraded to national park status in 2012 as part of an offset plan to compensate for the environmental impacts caused by the Bumbuna hydroelectric project (Brncic et al. 2010; Kormos et al. 2014). Loma Mountains National park is located in Sierra Leone’s Nothern Province (Forestry Division 2012). Mount Bintumani is located in the site, which, at 1,945 m, is the highest peak in West Africa, west of Mount Cameroon (Hanson-Alp et al. 2003). The high elevations in the area gave rise to three main plant communities: closed forests and savanna (from 4,60 to 915 m), sub-montane Shrubland and gallery forests (915 to 1,700 m), and montane grassland (above 1,700, Forestry Division 2012). In addition to the western chimpanzee, the site hosts other endangered and vulnerable species, including western red colobus (''Piliocolobus badius''), Diana monkey (''Cercopithecus diana''), pygmy hippo (''Choeropsis liberiensis''), golden cat (''Caracal aurata''), and zebra duiker (''Cephalophus zebra'', Forestry Division 2012). The site is also an Important Bird Area ([http://datazone.birdlife.org/site/factsheet/loma-mountains-non-hunting-forest-reserve-iba-sierra-leone IBA]) with at least 245 bird species (BirdLife International 2019).
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The site was first established as a non-hunting reserve in 1972, and upgraded to national park status in 2012 as part of an offset plan to compensate for the environmental impacts caused by the Bumbuna hydroelectric project (Brncic et al. 2010; Kormos et al. 2014). Loma Mountains National park is located in Sierra Leone’s Northern Province (Forestry Division 2012). Mount Bintumani is located in the site, which, at 1,945 m, is the highest peak in West Africa, west of Mount Cameroon (Hanson-Alp et al. 2003). The high elevations in the area gave rise to three main plant communities: closed forests and savanna (from 4,60 to 915 m), sub-montane Shrubland and gallery forests (915 to 1,700 m), and montane grassland (above 1,700, Forestry Division 2012). In addition to the western chimpanzee, the site hosts other endangered and vulnerable species, including western red colobus (''Piliocolobus badius''), Diana monkey (''Cercopithecus diana''), pygmy hippo (''Choeropsis liberiensis''), golden cat (''Caracal aurata''), and zebra duiker (''Cephalophus zebra'', Forestry Division 2012). The site is also an Important Bird Area ([http://datazone.birdlife.org/site/factsheet/loma-mountains-non-hunting-forest-reserve-iba-sierra-leone IBA]) with at least 245 bird species (BirdLife International 2019).
    
'''Table 1. Basic site information for Loma Mountains National Park'''
 
'''Table 1. Basic site information for Loma Mountains National Park'''
 
{| border="1" cellpadding="5" cellspacing="0" class="basic-information"
 
{| border="1" cellpadding="5" cellspacing="0" class="basic-information"
 
|Area            <!-- Please include units: km2/ha e.g 200ha    -->
 
|Area            <!-- Please include units: km2/ha e.g 200ha    -->
|332 km²
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|288.5 km²
 
|-
 
|-
 
|Coordinates
 
|Coordinates
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= Ape status =  <!-- a text overview of ape status (population sizes, trends etc), followed by a table of specific surveys and results -->
 
= Ape status =  <!-- a text overview of ape status (population sizes, trends etc), followed by a table of specific surveys and results -->
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According to a nationwide survey in 2009, which included Loma Mountains, an estimated 1,065 chimpanzees inhabit the site (Brncic et al. 2010). Loma is estimated to harbor 20% of the country’s chimpanzee population. The highest chimpanzee densities were found at higher elevations, likely because they are not easily accessed by humans (Brncic et al. 2010). The chimpanzee population trend is unknown, but based on a viability analysis, the population was projected to decline over the next 200 years if current conditions remained the same (Carlsen et al. 2011).
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According to a nationwide survey in 2009, which included Loma Mountains, an estimated 1,065 chimpanzees inhabit the site (Brncic et al. 2010). Loma is estimated to harbor 20% of the country’s chimpanzee population. The highest chimpanzee densities were found at higher elevations, likely because they are not easily accessed by humans (Brncic et al. 2010). Several studies targeting chimpanzee population status at this site have reported varying density and abundance estimates. A chimpanzee survey conducted in 2008 reported a density 5.75 chimpanzee / km2, and another conducted in 2010 documented chimpanzee density at 2.69 chimpanzee / km2. The most recent survey along systematically paced line transects confirmed a population density of 4.81 chimpanzee / km2 in 2019. The varying densities reported over the last one decade shows an increasingly higher chimpanzee population occurrence at LMNP as compared to other sites in West Africa.
    
'''Table 2. Ape population estimates in Loma Mountains National Park'''
 
'''Table 2. Ape population estimates in Loma Mountains National Park'''
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|Brncic et al. 2010
 
|Brncic et al. 2010
 
|Survey effort: 59.8 km
 
|Survey effort: 59.8 km
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|
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|-
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|''Pan troglodytes verus''
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|2019
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|1390 (819- 2361)
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|4.81 (2.83- 8.18)
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|10.03
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|Loma Mountains National Park 288.5 km2
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|Line transects (Distance)
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|Garriga 2019
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|35 transects were placed , but 34 transects were walked for a total of 66.08 km of survey effort
 
|
 
|
 
|}
 
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= Threats =    <!-- a text overview of threats, followed by a table of key threats -->
 
= Threats =    <!-- a text overview of threats, followed by a table of key threats -->
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During a chimpanzee survey in 2009, human activities were observed mostly in the lowland areas of the park, especially farming activities (Brncic et al. 2010). Similarly, hunting signs were less common at higher elevations, near Bintumani peak. Overall, hunting pressure is much lower in Loma Mountains National Park compared to Tingi Hills or WAPFR (Brncic et al. 2010). While local people considerably rely on bushmeat, most of it is obtained close to the fields, and larger animals account only for a smaller fraction of bushmeat consumed (Forestry Division 2012). However, the extent of commercial hunting in the area is unknown (Forestry Division 2012).
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During a chimpanzee survey in 2009, human activities were observed mostly in the lowland areas of the park, especially farming activities (Brncic et al. 2010). Similarly, hunting signs were less common at higher elevations, near Bintumani peak. Overall, hunting pressure is much lower in Loma Mountains National Park compared to Tingi Hills or WAPFR (Brncic et al. 2010). Human activity such as hunting either for subsistence or commercial purpose are predominant in the central areas, evidence from hunting trails, gun shells and snares, and farming activities more frequent near the park boundaries. However, less signs of human activities have been observed in the areas with higher chimpanzee nest encounters, mostly areas with steeper hills and more difficult access for humans (Garriga & Kanneh 2022). While local people considerably rely on bushmeat, most of it is obtained close to the fields, and larger animals account only for a smaller fraction of bushmeat consumed (Forestry Division 2012). Uncontrolled wildfire is also another serious threat to the ecosystem structure of the park that spread widely in the park at the peak of the dry season. During the 2019 survey, cleared and burnt areas of the forest (suspected source from farming activities and wild fire introduced by cattle herdsmen) close to the boundary and inside the park were frequently walked by the field team (Garriga 2019).
    
'''Table 3. Threats to great apes in Loma Mountains National Park'''
 
'''Table 3. Threats to great apes in Loma Mountains National Park'''
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|2. Agriculture & aquaculture
 
|2. Agriculture & aquaculture
 
|2.1 Annual & perennial non-timber crops
 
|2.1 Annual & perennial non-timber crops
|High
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|Present, but threat severity unknown
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|
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|Vegetation cleared for agriculture (Brncic et al. 2010, Forestry Division 2012). Farming along the park boundary and certain areas within the park exist, carried out by the forest edge community members (Garriga & Kanneh 2022).
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|Ongoing (2022)
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|-
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|2.3 Livestock farming & ranching
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|Present, but threat severity unknown
 
|15% of vegetation cleared
 
|15% of vegetation cleared
|Vegetation cleared for agriculture (Brncic et al. 2010, Forestry Division 2012)
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|Cattle rearing at the landscape is predominant mainly in the dry season (Garriga, 2019).
|Ongoing (2012)
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|Ongoing (2019)
 
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|-
 
|3. Energy production & mining
 
|3. Energy production & mining
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|5. Biological resource use
 
|5. Biological resource use
 
|5.1 Hunting & collecting terrestrial animals
 
|5.1 Hunting & collecting terrestrial animals
|Present
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|Present, but threat severity unknown
 
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|Hunting signs are present in the lowland areas of the park (Brncic et al. 2010)
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|Hunting (hunting trails, gun shells and snares) (Garriga 2019).
|Ongoing (2010)
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|Ongoing (2019)
 
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|-
 
|
 
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|7. Natural system modifications
 
|7. Natural system modifications
 
|7.1 Fire & fire suppression
 
|7.1 Fire & fire suppression
|Present
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|Present, but threat severity unknown
 
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|Fires to clear vegetation within and around the park sometimes extend beyond the intended field (Forestry Division 2012)
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|Fires to clear vegetation within and around the park sometimes extend beyond the intended field (Forestry Division 2012). Wildfire is also a common threat to the forest ecosystem. This is more frequent in the dry season, and the fire is mostly put on by the cattle herders for fresh and young nutritious grass for their cattle (Garriga & Kanneh 2022).
|Ongoing (2012)
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|Ongoing (2022)
 
|-
 
|-
 
|8. Invasive & other problematic species, genes, diseases
 
|8. Invasive & other problematic species, genes, diseases
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The Forestry Division of Sierra Leone is responsible for the management of protected areas (Forestry Division 2012). The World Bank provided initial funding for the setup of the national park, but the long-term, sustainable financing of the park has not been secured (Kormos et al. 2014; Forestry Division 2012). Conservation measures for the park have included the development of a management plan, demarcation of the park’s boundaries, and posting and training staff (Kormos et al. 2014).
 
The Forestry Division of Sierra Leone is responsible for the management of protected areas (Forestry Division 2012). The World Bank provided initial funding for the setup of the national park, but the long-term, sustainable financing of the park has not been secured (Kormos et al. 2014; Forestry Division 2012). Conservation measures for the park have included the development of a management plan, demarcation of the park’s boundaries, and posting and training staff (Kormos et al. 2014).
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The conservation activities undertaken within and outside the park have been restored since 2019 with one year funds from the US Fish and Wildlife Service through TCS to protect the remaining population of western chimpanzees thriving in the park. Since 2019, lots of conservation interventions are ongoing to support the protection of the park and sustain the long-term conservation of the remaining population of western chimpanzees. Before the intervention of TCS in 2019, the Biodiversity Conservation Project (BCP) was implemented that led to the construction of the park centre and other conservation interventions (Garriga & Kanneh 2022).
    
'''Table 4. Conservation activities in Loma Mountains National Park'''
 
'''Table 4. Conservation activities in Loma Mountains National Park'''
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|As of 2012, two rangers were part of the park’s staff (Forestry Division 2012)
 
|As of 2012, two rangers were part of the park’s staff (Forestry Division 2012)
 
|Since 2012
 
|Since 2012
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|-
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|
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|5.11. Provide training to anti-poaching ranger patrols
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|Training for bio-monitors, TKEEP teachers coordinators and local farmers to support capacity building. The community bio-monitors periodically received training on data collection procedures on wildlife and human signs and activities, and forest patrol techniques. Likewise the TKEEP Teachers coordinators on education following the TKEEP work book. And the farmers on sustainable agricultural practices (Garriga & Kanneh 2022).
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|Ongoing (2019)
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|-
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|
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|5.15. Implement monitoring surveillance strategies (e.g. SMART) or use monitoring data to improve effectiveness of wildlife law enforcement patrols
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|Law enforcement through active forest patrols. The National Protected Area Authority (NPAA) game guards working in conjunction with the Tacugama community bio-monitors patrol the park and its territories while collecting data on human activities and wildlife presence (Garriga & Kanneh 2022).
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|Ongoing (2019)
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|-
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|
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|5.16. Implement community control of patrolling, banning hunting and removing snares
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|Active bio-monitoring to support research activities: Since 2019 to date there have been well-planned and active bio-monitoring activities undertaken by the TCS community bio-monitors with the LMNP. The biomonitoring employs specialised software programs (SMART, CyberTracker and Gaia GPS) installed on android mobile devices for data collection on wildlife and human activities presence and distribution within the park (Garriga & Kanneh 2022).
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|Ongoing (2019)
 
|-
 
|-
 
|6. Human intrusions & disturbance
 
|6. Human intrusions & disturbance
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|-
 
|-
 
|10. Education & Awareness  
 
|10. Education & Awareness  
|Not reported
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|10.1. Educate local communities about primates and sustainable use
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|Conservation education in selected schools of the park communities: TCS have extended its education program in the schools working with the schools kids and teacher coordinators to fully implement its Tacugama Kids Environmental Education Program (TKEEP) workbook at the beginning/end of every school year since 2020 (Garriga & Kanneh 2022).
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|Ongoing (2019)
 
|-
 
|-
 
|11. Habitat Protection
 
|11. Habitat Protection
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|11.6. Demarcate and enforce boundaries of protected areas
 
|11.6. Demarcate and enforce boundaries of protected areas
 
|Resurveying and physically demarcating park boundary (Kormos et al. 2014)
 
|Resurveying and physically demarcating park boundary (Kormos et al. 2014)
|Ongoing(2014)
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|Ongoing (2014)
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|-
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|
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|11.9. Plant indigenous fast-growing trees (will not necessarily resemble original community) in clear-cut areas
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|Reforestation: tree planting of native species with high survival rate occurring at the park region. Every year since 2019 to date, the Tacugama Chimpanzee Sanctuary (TCS) organised the local community members and engaged them in tree planting of degraded areas along the park boundary in the months of July and August  (Garriga & Kanneh 2022).
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|Ongoing (2019)
 
|-
 
|-
 
|12. Species Management
 
|12. Species Management
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|-
 
|-
 
|13. Livelihood; Economic & Other Incentives  
 
|13. Livelihood; Economic & Other Incentives  
|Not reported
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|13.2. Provide non-monetary benefits to local communities for sustainably managing their forest and its wildlife (e.g. better education, infrastructure development)
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|Agriculture: support with agricultural inputs (groundnut and rice seeds and tools) for cultivation. Livelihood support to the park communities in the form of agricultural seeds, tools and sustainable cultivation practices training to farmers groups. The community members who practise farming have been formed into small groups (farmer groups) and are supported with the required agriculture inputs every year since 2019 (Garriga & Kanneh 2022).
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|Ongoing (2019)
 
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|-
 
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= Challenges = <!-- Overview of impediments to ape conservation -->
 
= Challenges = <!-- Overview of impediments to ape conservation -->
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Conservation funds to finance the operation of the park for long term meeting community livelihoods: although there are ongoing livelihood activities, the resources are limited to adequately respond to many needs of the residing park communities mainly in terms of infrastructure and other basic needs of life (Garriga & Kanneh 2022).
    
'''Table 5. Challenges reported for Loma Mountains National Park'''
 
'''Table 5. Challenges reported for Loma Mountains National Park'''
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|Lack of financial means
 
|Lack of financial means
 
|Kormos et al. 2014
 
|Kormos et al. 2014
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|-
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|Lack of national protection
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|Garriga & Kanneh 2022
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|-
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|Lack of logistical means
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|Garriga & Kanneh 2022
 
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= Research activities = <!-- Overview of research activities -->
 
= Research activities = <!-- Overview of research activities -->
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No information on research activities has been documented.  
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Research activities include: chimpanzee surveys using systematically placed line transect throughout the park; bio-monitoring using the SMART and CyberTracker applications; environmental education and sensitizations on the Sierra Leone National Animal – National Animal Campaign through questionnaire and survey led by Tacugama within the park communities (Garriga & Kanneh 2022).
 
      
===Documented behaviours===  <!-- List of any behaviours observed at the site, including citations -->
 
===Documented behaviours===  <!-- List of any behaviours observed at the site, including citations -->
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Forestry Division. 2012. Loma Mountains National Park: Preliminary Management Plan 2013-2017. Ministry of Agriculture, Forestry and Food Security, Sierra Leone<br>
 
Forestry Division. 2012. Loma Mountains National Park: Preliminary Management Plan 2013-2017. Ministry of Agriculture, Forestry and Food Security, Sierra Leone<br>
 
Hanson-Alp, R., Bakarr, M.I., Lebbie, A., Bangura, K.I. 2003. West African Chimpanzees. Status Survey and Conservation Action Plan, Chapter 10: Sierra Leone. IUCN/SSC Primate Specialist Group. IUCN, Gland, Switzerland and Cambridge, UK<br>
 
Hanson-Alp, R., Bakarr, M.I., Lebbie, A., Bangura, K.I. 2003. West African Chimpanzees. Status Survey and Conservation Action Plan, Chapter 10: Sierra Leone. IUCN/SSC Primate Specialist Group. IUCN, Gland, Switzerland and Cambridge, UK<br>
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Garriga R.M., (2019). Loma Mountains National Park Chimpanzee Nest Survey, Report, Tacugama Chimpanzee Sanctuary. Freetown, Sierra Leone. 25p<br>
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Garriga, R. & Kanneh, A. (2022, October 20-21). Sierra Leone. Regional workshop on IUCN APES wiki, Monrovia, Liberia.
 
Kormos R, Kormos CF, Humle T, Lanjouw A, Rainer H, et al. 2014. Great Apes and Biodiversity Offset Projects in Africa: The Case for National Offset Strategies. PLOS ONE 9(11): e111671. https://doi.org/10.1371/journal.pone.0111671<br>
 
Kormos R, Kormos CF, Humle T, Lanjouw A, Rainer H, et al. 2014. Great Apes and Biodiversity Offset Projects in Africa: The Case for National Offset Strategies. PLOS ONE 9(11): e111671. https://doi.org/10.1371/journal.pone.0111671<br>
       
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'''Page completed by:''' A.P.E.S. Wiki Team '''Date:''' 02/09/2019 <!-- If you don't want to add your name, you can add "A.P.E.S. Wiki team" -->
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'''Page completed by:''' Ambrose Bockarie Kanneh & Rosa M. Garriga '''Date:''' 25/01/2023 <!-- If you don't want to add your name, you can add "A.P.E.S. Wiki team" -->
 
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