Mount Hamiguitan Range Wildlife Sanctuary
Country
Philippines
Inscribed in
2014
Criterion
(x)
The conservation outlook for this site has been assessed as "good" 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.
Forming a mountain ridge running north-south along the Pujada Peninsula in the south-eastern part of the Eastern Mindanao Biodiversity Corridor, the Mount Hamiguitan Range Wildlife Sanctuary has an elevation range of 75–1,637 m above sea level and provides critical habitat for a range of plant and animal species. The property showcases terrestrial and aquatic habitats at different elevations, and includes threatened and endemic flora and fauna species, eight of which are found only at Mount Hamiguitan. These include critically endangered trees, plants and the iconic Philippine eagle and Philippine cockatoo.
© UNESCO
Summary
2025 Conservation Outlook
Finalised on
11 Oct 2025
Good
Current state and trend of VALUES
Low Concern
Overall THREATS
Overall PROTECTION and MANAGEMENT
Full assessment
Description of values
Critical habitat for a range of plant and animal species within the globally significant Philippine Biodiversity Hotspot
Criterion
(x)
The Mt. Hamiguitan Range Wildlife Sanctuary (MHRWS) represents a complete, substantially intact and highly diverse mountain ecosystem in a globally significant biogeographic region of the Philippines. The World Heritage site is home to both terrestrial and aquatic habitats, at a series of different elevations characterized by highly dissimilar soil and climate conditions. Five vegetation types exist within the site; agro-ecosystems on lower elevations, dipterocarp forests, montane forests and mossy forests on higher elevations and mountain slopes, and mossy-pygmy forests on the highest windswept mountaintops (IUCN, 2014). These ecosystem types houses animal species representing all the animal groups found in the site as well as relatively recently discovered species. As a result of its semi-isolation and its varied habitat types growing in dissimilar soil and climate conditions, its biodiversity has shown a significantly high level of endemicity (World Heritage Committee, 2014).
Critically endangered trees and plants
Criterion
(x)
The MHRWS provides a sanctuary to a host of globally threatened and endemic flora and fauna species, eight of which are found nowhere else except Mount Hamiguitan. These include critically endangered trees and plants such as the trees Shorea polysperma and Shorea astylosa, and the orchid Paphiopedilum adductum. Its diversity of plants and animals include globally threatened species as well as a large number of endemic species including those species that exist only in the Philippines, only in Mindanao and only in the World Heritage site. The fragile tropical “bonsai” forest that crowns the Mount Hamiguitan Range Wildlife Sanctuary epitomizes nature’s bid to survive in adverse conditions (World Heritage Committee, 2014).
Large species diversity and high level of endemism
Criterion
(x)
The combination of terrestrial and aquatic ecosystems within the boundaries of the World Heritage site and the large number of species inhabiting each makes the Mount Hamiguitan Range Wildlife Sanctuary very rich in species diversity. It is home to a total of 1,380 species with 341 Philippine endemics that include critically endangered species such as the iconic Philippine eagle (Pithecophaga jefferyi) and the Philippine cockatoo (Cacatua haematuropygia) (World Heritage Committee, 2014). The site supports a high percentage of the bird (20%), amphibian (20%), mammal (16%), reptile (14%) and plant (10%) species within the Philippines Biodiversity Hotspot (UNEP-WCMC, 2012), and its high level of endemicity is well exemplified by the proportion of its amphibian (75% endemic) and reptile (84% endemic) species (World Heritage Committee, 2014).
Assessment information
The World Heritage site overall is well preserved and intact. It is in a relatively pristine condition and thus relatively free from current threats. It has laws that prohibit incompatible activities such as logging, mining, exploration or surveying for energy resources inside Mount Hamiguitan Range Wildlife Sanctuary (MHRWS). The protection of the site is further strengthened by the engagement with and involvement of local and indigenous communities living in its periphery (World Heritage Committee, 2014). However, natural habitats especially in the southern portion of the site are vulnerable to conversion of land for agriculture.
Residential Areas
(Housing areas)
Inside site
, Localised(<5%)
Outside site
At the time of the initial nomination, the State Party estimated that less than 100 people lived within the Mt. Hamiguitan Range Wildlife Sanctuary (MHRWS) and only small numbers in the buffer zone (State Party of the Philippines, 2012). This number has grown, along with the expansion of the site, with the Protected Area Management Office recording a total of 658 households within the original and expanded World Heritage site through the Socio-Economic Assessment and Monitoring System (SEAMS). However, the livelihoods of these communities are well considered and integrated into the management of the site, such that the threat is likely to be minimised through effective initiatives and management interventions to provide benefits to the local community while, simultaneously, mitigate any potentially negative effects on the values of the site brought about by development (IUCN Consultation, 2020a). There are estimated to be fewer than 100 inhabitants within the core zone of the property and again, fewer than 100 residing within the buffer zone. In total these 184 residents are permitted to live inside the property and its buffer zone because they attained their tenurial instruments or permits prior to the declaration of the property as a protected area. No current numbers are available for people living within the site but as noted previously communities are well integrated into the management of the site and impacts are likely to be minimal on the World heritage values.
Recreational Activities
(Impact of tourism)
Inside site
, Localised(<5%)
There are strict controls over access to the site. In pursuit of establishing sustainable financing mechanisms and promote sustainable livelihoods to the communities, the Protected Area Management Board (PAMB) decided to lift the closure of MHRWS to trekking and mountaineering in 2017 (IUCN Consultation, 2020a). However, the policy mitigates against potential associated threats through protocols and restrictions to maintain the site's integrity and values. For example, visitor entry is limited to 30 heads per climb and only within the established trails and campsites as described in Volume 2 of the Nomination Dossier of MHRWS.
The management plan for the site was due for renewal in 2020, however, no updated management plan could be located for this assessment. When revised the management plan must continue to align with tourism and development plans of the overlapping municipalities, helping to ensure the importance of the protection of the site (World Heritage Committee, 2014) and continuing the efforts to limit the impact of tourism on the site and its values.
The management plan for the site was due for renewal in 2020, however, no updated management plan could be located for this assessment. When revised the management plan must continue to align with tourism and development plans of the overlapping municipalities, helping to ensure the importance of the protection of the site (World Heritage Committee, 2014) and continuing the efforts to limit the impact of tourism on the site and its values.
Mining & Quarrying
(Mining operations in and adjacent to the buffer zone; mineral exploration)
Outside site
Mining operations continue in and adjacent to the buffer zone. However, there has been progress made in terms of management and agreements have been set up between mining lease-holders and the mining company to cooperate with respect to protection of important habitats. In addition, some mining lease proposals have been refused at the local governmental level (IUCN, 2014). The PAMB was working on the legislation of the enlarged World Heritage site to be part of the entirety of the original area (7,132.76 hectares) previously declared under Republic Act No. 9303. In doing so the expansion would secure the entire site from any prospective mining claims, including within the buffer zone (IUCN Consultation, 2020a). The status of this legislation is unclear. Prohibited mining activities also seem to continue in secret with the potential involvement of political leaders in this activity (Celeste, 2021).
Logging, Harvesting & Controlling Trees
(Illegal collection of species and illegal removal of timber often associated with mining)
Inside site
, Extent of threat not known
Outside site
Threats in and around the World Heritage site include the illegal collection of wildlife and the illegal removal of timber and non-timber forest products. The protection of the site is strengthened by the engagement with and involvement of local and indigenous communities living in the periphery of the site in its management. These include successful sustainable development and rehabilitation activities, which are undertaken by the Philippine Department of Environment and Natural Resources (DENR) and in particular, the Biodiversity Management Bureau (BMB) of the Philippine DENR and the Protected Area Management Board (PAMB) (State Party of the Philippines, 2012). However, Celsete (2021) stresses that apprehensive activities like illegal logging done by both small and large scale companies are still prevalent. Prohibited mining activities also seem to continue in secret with the potential involvement of political leaders in this activity. Thus, current protection efforts are not fully successful because problems continue to exist despite this implementation (Celeste, 2021).
Annual & Perennial Non-Timber Crops, Terrestrial Animal Farming, Ranching & Herding
(Conversion of land for agriculture in lowland areas within the buffer zone)
Inside site
, Extent of threat not known
Outside site
The conversion of land for agriculture and the use of slash-and-burn farming (kaingin) has been detected in the buffer zone in the past. The State Party continues to work collaboratively with local communities and indigenous peoples on the management of the World Heritage site to resolve any outstanding land claims (World Heritage Committee, 2014) and to address the expansion of land for agriculture. The relationship with local communities is strong and this is likely to help limit the impact of this conversion in the buffer zone but if that situation changes impacts could again arise. Although the northern part (or the original extent of the Wildlife Sanctuary) is relatively well protected and managed, as previously observed by Supsup et al. (2017), natural habitats in the extended southern portion of the site are highly vulnerable to conversion, which has the potential to become a high threat. Evidence points to some issues in apprehending illegal loggers (Celeste, 2021).
Two issues have been identified as the most significant potential threats to the site: climate change and increased tourism access. Climate change has the potential to seriously impact on the vegetation of the MHRWS, which is highly elevation and soil condition dependent and thus sensitive to precipitation and temperature variations. The State Party has put in place the MHRWS Monitoring Assessment Programme for Climate Change Adaptation to consider the potential impact of climate change. The site was closed to tourism access pending finalization of a trail management plan but it is unclear if this has been completed and tourism is now permitted. However, the increased demand for access following inscription may lead to increased pressure on MHRWS’s sensitive ecological communities. A Tourism Management plan has been developed to plan for the threat of increasing tourism. Martial Law is no longer in force within Mindanao, and conflict is likely to have been alleviated without having had significant impacts on the World Heritage site. For now, this remains a potential threat, as it is difficult to predict how the situation might unfold in the future.
Recreational Activities
(Potential impacts from increased visitation)
Inside site
, Extent of threat not known
The inscription of the site on the World Heritage list may result in pressure to provide access and an increase in visitation. Tourism related activities may directly impact on the site and resources within the park. Issues that may arise include pollution and waste management (IUCN, 2014). Plans have been developed to address this and currently there appears to be strong management of visitation and limited impacts from the numbers allowed to enter the site.
Conflict, Civil Unrest & Security Activities
(Siege of Marawi city and martial law in Mindanao)
Outside site
The conflict, which arose around Marawi City and subsequent enforcement of Martial law in Mindanao, carried the potential for rebel forces or terrorist groups or individuals to the use the Wildlife Sanctuary as a retreat area along with other disturbances associated with conflict zones. However, there are no existing data to support its potential impact on the site (IUCN Consultation, 2020b).
Martial law has now been withdrawn from the island, alleviating this particular threat in the immediate term. However, it is important to track the ongoing situation as the post-Martial Law period may bring new challenges to the site.
Martial law has now been withdrawn from the island, alleviating this particular threat in the immediate term. However, it is important to track the ongoing situation as the post-Martial Law period may bring new challenges to the site.
Changes in Physical & Chemical Regimes, Changes in Temperature Regimes, Changes in Precipitation & Hydrological Regime
(Temperate extremes / habitat changes / increase in extreme weather events)
Inside site
, Widespread(15-50%)
MHRWS is not currently subject to detectable significant impacts from climate change. Nonetheless, there are likely impacts of climate change on species' compositions, ranges, seasonal cycles, habitat preferences, increased precipitation and extreme weather events. Changes to weather patterns and a higher frequency and intensity of natural disasters such as landslides, storms and droughts could affect the site in the future (IUCN, 2014). Monitoring and Assessment Program for Climate Change Adaption was being carried out by the Technical Group for the continued socio-cultural, economic, and ecological study in Mount Hamiguitan Range, led by the Davao Oriental State College of Science and Technology. The information derived from the programme should be used for the maintenance of biodiversity and to safeguard ecosystems. It likewise examines trends in the ecological status of the existing ecosystems and species in the area (State Party of the Philippines, 2012) and further monitoring should be conducted within the site to detect and changes potentially caused by changes to climate.
Involvement of stakeholders and rightsholders, including indigenous peoples and local communities, in decision-making processes
The MHRWS has experienced periods of strong stakeholder participation, however engagement has diminished over time. Nonetheless, it holds the potential for revival and renewed collaboration (Cereno and Roxas, 2025).
Impressive levels of local community and NGO involvement were evident in the World Heritage site, most notably in the Municipality of San Isidro (IUCN, 2014). The protection of the MHRWS was further strengthened by engagement with and involvement of local and indigenous communities living in its periphery. Their lifestyles and spiritual beliefs are based on respect for the environment and its biodiversity and they have, over time, subtly molded their way of life to ensure the sustainable use of their resources. Local managers continue efforts to work collaboratively with local communities and indigenous peoples on the management of the World Heritage site and to ensure the equitable access and sharing of benefits, including those that may accrue from tourism (World Heritage Committee, 2014). The Philippine National Commission for Indigenous Peoples (NCIP) continues to resolve any outstanding land claims, while Province of Davao Oriental continues actively engaging the communities of indigenous peoples in villages located in Mati City and the Municipality of Governor Generoso. The indigenous communities recognize that the inscription of the MHRWS contributes to the protection of the mountain (State Party of the Philippines, 2012). Nevertheless, various reasons impede people’s participation in the overall protection and conservation. One of the main reasons is the socio-economic reliance on natural resources within the forest. The need for providing alternative livelihoods is evident (Celeste, 2021). The lack of community participation also contributes to the non-effective monitoring and problems with the protection of the forest in general. This is because not all community members attend meetings, lectures, and fora relating to their forest protection and management (Celeste, 2021). Furthermore, challenges remain in clarifying property rights including inactive POs, expired community/based forest management agreements, and the lack of tenured migrant representation in the protected area management board, PAMB (Cereno and Roxas, 2025). The MHRWS-PAMB faces significant challenges regarding stakeholder representation, specifically the lack of Indigenous Peoples representation and the limited participation of tenured farmers. The PAMB has lacked an Indigenous Peoples representative for a year due to pending municipal resolutions from LGUs. This absence means Indigenous Peoples have no voice in decision-making (Cereno and Roxas, 2025).
Impressive levels of local community and NGO involvement were evident in the World Heritage site, most notably in the Municipality of San Isidro (IUCN, 2014). The protection of the MHRWS was further strengthened by engagement with and involvement of local and indigenous communities living in its periphery. Their lifestyles and spiritual beliefs are based on respect for the environment and its biodiversity and they have, over time, subtly molded their way of life to ensure the sustainable use of their resources. Local managers continue efforts to work collaboratively with local communities and indigenous peoples on the management of the World Heritage site and to ensure the equitable access and sharing of benefits, including those that may accrue from tourism (World Heritage Committee, 2014). The Philippine National Commission for Indigenous Peoples (NCIP) continues to resolve any outstanding land claims, while Province of Davao Oriental continues actively engaging the communities of indigenous peoples in villages located in Mati City and the Municipality of Governor Generoso. The indigenous communities recognize that the inscription of the MHRWS contributes to the protection of the mountain (State Party of the Philippines, 2012). Nevertheless, various reasons impede people’s participation in the overall protection and conservation. One of the main reasons is the socio-economic reliance on natural resources within the forest. The need for providing alternative livelihoods is evident (Celeste, 2021). The lack of community participation also contributes to the non-effective monitoring and problems with the protection of the forest in general. This is because not all community members attend meetings, lectures, and fora relating to their forest protection and management (Celeste, 2021). Furthermore, challenges remain in clarifying property rights including inactive POs, expired community/based forest management agreements, and the lack of tenured migrant representation in the protected area management board, PAMB (Cereno and Roxas, 2025). The MHRWS-PAMB faces significant challenges regarding stakeholder representation, specifically the lack of Indigenous Peoples representation and the limited participation of tenured farmers. The PAMB has lacked an Indigenous Peoples representative for a year due to pending municipal resolutions from LGUs. This absence means Indigenous Peoples have no voice in decision-making (Cereno and Roxas, 2025).
Legal framework
The MHRWS is protected through several protected area regulations and is a component of the Philippines’ National Integrated Protected Areas System (NIPAS). Several layers of national and provincial legislation and policies serve to protect the World Heritage site and guide management. Apart from delineating the boundaries of the site, these laws prohibit incompatible activities such as logging, mining, exploration or surveying for energy resources inside the site. Responsibility for enforcement is shared by both the national and local government agencies in partnership with other stakeholders (World Heritage Committee, 2014). Progress has been made towards legislation, which would deem mining illegal within the site and its buffer zone. The Regional Development Council of the National Economic Development Authority of Region XI has been coordinating with the legislative branch of the national government to facilitate the law-making process while the PAMB is administering the compliance of requirements as prescribed by the law. The full legislation of the site will ultimately secure it from any prospective mining claims, even in the buffer zone (IUCN Consultation, 2020a).
Governance arrangements
The World Heritage site straddles two municipalities and one city: San Isidro Municipality, Governor Generoso Municipality and the City of Mati, in the Province of Davao Oriental (World Heritage Committee, 2014). MHRWS is a component of the Philippines’ National Integrated Protected Areas System (NIPAS).
The property is split into two zones: i) the Strict Protection Zone, where human activity is limited to scientific studies and visitors are under the strict guidance of rangers; and ii) a Buffer Zone, which surrounds the Strict Protection Zone and where restrictions are not so stringent. The Mount Hamiguitan Protected Area Management Board (PAMB) oversees protection and management of the property according to the approved Management Plan.
The PAMB consists of six members: Regional Executive Director, Governor and provincial planning officer of Davao Oriental, the Mayors of the three municipalities, Barangay Captains of village centres in the property and tribal chieftains of indigenous peoples. The Protected Area Superintendent’s Office (PASO) is composed of a technical and administrative team, which provide a predominantly managerial role and a team of support staff, who function as wardens, and patrols staff.
The PASO implements the activities set down in the plan as well as the policies and directives issued by the PAMB. Together with the “Bantay Gubat” personnel from the three municipalities with territorial jurisdiction over the property, the PASO conducts regular monitoring and patrol activities over the core and buffer zones.
The property is split into two zones: i) the Strict Protection Zone, where human activity is limited to scientific studies and visitors are under the strict guidance of rangers; and ii) a Buffer Zone, which surrounds the Strict Protection Zone and where restrictions are not so stringent. The Mount Hamiguitan Protected Area Management Board (PAMB) oversees protection and management of the property according to the approved Management Plan.
The PAMB consists of six members: Regional Executive Director, Governor and provincial planning officer of Davao Oriental, the Mayors of the three municipalities, Barangay Captains of village centres in the property and tribal chieftains of indigenous peoples. The Protected Area Superintendent’s Office (PASO) is composed of a technical and administrative team, which provide a predominantly managerial role and a team of support staff, who function as wardens, and patrols staff.
The PASO implements the activities set down in the plan as well as the policies and directives issued by the PAMB. Together with the “Bantay Gubat” personnel from the three municipalities with territorial jurisdiction over the property, the PASO conducts regular monitoring and patrol activities over the core and buffer zones.
Integration into local, regional and national planning systems (including sea/landscape connectivity)
The World Heritage site straddles two municipalities and one city: San Isidro Municipality, Governor Generoso Municipality and the City of Mati, in the Province of Davao Oriental (World Heritage Committee, 2014). MHRWS is a component of the Philippines’ National Integrated Protected Areas System (NIPAS). The laws defining and affecting the site provide for a complementary and generally harmonized level of protection of the site. The laws control development within the boundaries of the site and are consistent in their objectives to protect the site's key values. Agro-forestry operations intersperse with remnants of the natural forests within the buffer zone and are covered by Community-Based Forestry Management Agreements (CBFMA) and Certificate of Stewardship Contracts (CSC) (IUCN, 2014; World Heritage Committee, 2014).
Boundaries
The World Heritage site totals an area of 16,923 ha with a buffer zone of 9,729 ha. The boundaries of the site are delineated under legal instruments ensuring protection and management of the site and preventing physical interventions, such as logging, mining exploration or surveying for energy resources. Enforcement responsibilities are shared between national and local governments in partnership with local stakeholders including local and indigenous communities living in the periphery of the Mount Hamiguitan Range Wildlife Sanctuary (MHRWS) (IUCN, 2014; World Heritage Committee, 2014). While the boundaries of the site largely follow those of the MHRWS, given its relatively small size, it will be important to ensure that other areas with adequate protection exist beyond the site in order to ensure effective conservation of those species with large range, particularly the Philippine Eagle (IUCN Consultation, 2020a).
Overlapping international designations
The property is particularly important for several high profile species of conservation concern, notably the Philippine eagle and Philippine cockatoo. The presence of these species, in addition to several others, has led the area to be classed as an Important Bird Area (IBA) by BirdLife International.
Implementation of World Heritage Committee decisions and recommendations
The State Party has been very responsive in addressing Committee decisions, specifically related to the 2013 referral recommendation. The Committee commended the State Party and stakeholders for the efficient and effective action to address concerns related to integrity, protection and management (World Heritage Committee, 2014). There have been no direct decisions for the property since then but there is no indication that the State Party would not remain very responsive.
Climate action
Management authorities have implemented a monitoring and research programme to anticipate climate change effects on the biota and to try to mitigate consequent impacts. Ongoing monitoring of threatened and rare plant and animal species was being carried out on an annual basis (State Party of the Philippines, 2014; World Heritage Committee, 2014). The MHRWS Monitoring & Assessment Programme for Climate Change Adaptation aims to better understand the impacts of climate change on the site’s ecological processes, species and abiotic elements. It represents a well-developed, science based strategy to combat the potentially unknown impacts of climate variability and recognizes the potential for climate change impact on the vertical zonation of the site’s vegetation communities. It also attempts to factor in anticipated impacts from visitation (World Heritage Committee, 2014). However, the level to which the findings of this work are being integrated into management decisions is unclear.
Management plan and overall management system
The World Heritage site consists of land classified as timberland under Land Classification Map Nos. 2660 and 2687 and as such belongs to the state. It is managed by a number of Government agencies including national Government agencies, Provincial level agencies and local community organizations with DENR assigned as its administrator (IUCN, 2014). The Protected Area Management Board (PAMB) oversees protection and management of the site according to the management plan, which was renewed in 2020 (IUCN Consultation, 2020a) and is due for renewal in 2024, although no updated plan could be identified.
In 2018, the PAMB carried out a Management Effectiveness Assessment (METT) for the site. The assessment found the management to be 75% effective, which represented a 7% increase from the 2014 assessment, which was carried out at around the same time as its inscription on the World Heritage list. According to the assessment, staffing (permanent staff and capacity development), communication, education and public awareness (CEPA), infrastructure/ facilities, sustainable financing, participatory and comprehensive management planning and decision-making, and research studies that contribute to decision-making were areas of potential improvement (IUCN Consultation, 2020a). It was also noted that threats related to agriculture and utilization of non-timber forest products must be addressed by the management (IUCN Consultation, 2020a).
In 2018, the PAMB carried out a Management Effectiveness Assessment (METT) for the site. The assessment found the management to be 75% effective, which represented a 7% increase from the 2014 assessment, which was carried out at around the same time as its inscription on the World Heritage list. According to the assessment, staffing (permanent staff and capacity development), communication, education and public awareness (CEPA), infrastructure/ facilities, sustainable financing, participatory and comprehensive management planning and decision-making, and research studies that contribute to decision-making were areas of potential improvement (IUCN Consultation, 2020a). It was also noted that threats related to agriculture and utilization of non-timber forest products must be addressed by the management (IUCN Consultation, 2020a).
Law enforcement
Law enforcement is carried out primarily by the Protected Area Management Office (PAMO), with the support of The Department of Environment and Natural Resources (DENR) through its Community Environment and Natural Resources Offices and Local Government. Law enforcement activities include patrolling and monitoring inside the World Heritage site by Bantay Gubat and Park Rangers using smartphone technology to track instances of breaches. The DENR and the PAMO have been effecting paralegal training for the Bantay Gubat or Park Ranger and other volunteers to capacitate them on law enforcement activities. Camera traps installed by PAMO at strategic locations in the park also detect human activity inside the boundaries to monitor any potential breaches of law or park protocol. However, there is little data to confirm the efficacy of these measures and there are reports of limited staff, support and capacity to implement and fully realize the programs outlined in the management plan (IUCN Consultation, 2020b). Overall, although policies are good, the problem boils down to the lack of human capacities which is perceived to hinder the successful monitoring of unlawful activities in the area (Celeste, 2021).
Sustainable finance
Despite recent increases in staffing and resources and an obvious commitment from Provincial authorities to the management of the site's staffing levels, resources and capacity remain low. At the time of the field evaluation 583,000 USD p.a. was being spent on management with funding coming from a combination of sources including the national government and the Provincial governments of Davao Oriental and the three municipalities of MHRWS (IUCN, 2014). Recently, tourism has been opened up within the site to provide an additional source of income for the park management, however the level of additional resources provided as compared to the increasing need for management that comes with visitation is unclear. Other avenues for generating income including payments for ecosystem services, an adopt-a-wildlife species project, and public-private partnership, among others have also been investigated (IUCN Consultation, 2020a). However, there is no evidence that these have been implemented to date. Recent studies indicate that the MHRWS continues to face challenges due to a decline in its budget, impacting its ability to manage and conserve the protected area effectively (Cereno and Roxas, 2025). LGU funding is currently limited to allocations from Mati, while requests for financing from Governor Generoso and San Isidro remain pending. This is possibly due to shifting priorities under new leadership, and frequent leadership changes. International donor support has also waned, with only UNESCO granting ₱2million to DOrSU for extension projects and the ASEAN Heritage Parks providing funds through DENR-BMB for protected areas, including MHRWS. However, key informants are unaware of the specific details regarding the allocation or basis for MHRWS funding from this source. This lack of transparency regarding funding may lead to trust issues and hinder the implementation of conservation initiatives (Cereno and Roxas, 2025).
Staff capacity, training and development
Staff of the protected area have undergone numerous training and development courses since the inscription of the site across a wide range of issues related to the management of the site (IUCN Consultation, 2020a). However, staff capacity was also assessed in the most recent management effectiveness assessment and identified as an area for improvement (IUCN Consultation, 2020a). Staff capacity is an essential component of site protection and management. Although a couple of personnel are currently conducting monitoring and patrolling activities in the site, measured impact/effectiveness of patrolling in terms of overall management remains unknown. Programs outlined in the management plan of the site are well crafted, however, with limited staff, support and capacity, its implementation cannot be fully realized (IUCN Consultation, 2020b). Bantay Gubat do not have a sustainable income from their work as forest guards (Celeste, 2021) and evidence points to only 2 Bantay Gubat enforcers assigned to patrol a 5000-hectare forest. Some of these areas that are unprotected are said to be the den of unlawful activities like illegal logging and hunting of animals (Celeste, 2021).
Education and interpretation programmes
As visitation to the World Heritage site is strictly controlled, with the number of visitors limited, interpretation and education is carried out mainly through the Mt. Hamiguitan World Heritage Park, established by the Provincial Government of Davao Oriental in the Municipality of San Isidro. The park serves as an interpretation site for MHRWS and handles the majority of visitors of Mount Hamiguitan for a day tour learning activity. The Protected Area Management Office, in collaboration with the Local Government Units, Academic Institutions and Non-Government Organizations, have been regularly implementing Communication, Education and Public Awareness (CEPA) campaign programs in MHRWS. To this end, a CEPA Plan was due to be formulated in order to formally integrate education and interpretation into the overall management of the site (IUCN Consultation, 2020a). It is unclear if this plan was completed and whether it is currently being implemented.
Tourism and visitation management
Tourism and visitation to the World Heritage site had increased in the past few years, having been previously closed to public visitation pending completion of a trail management plan. The current level of visitation, post the COVID-19 pandemic is unclear and visitation may not have rebounded to the same levels as prior to the pandemic.
The “Guidelines for Trekking, Mountaineering and Other Activities in MHRWS” was formulated, and visitation is now permitted within the site, although strictly following the protocols set out in the guidelines. The Guidelines set out the regulations in order to maintain the integrity of the site whilst providing opportunities for the local communities to sustainably earn and continue to steward the MHRWS simultaneously. A Tourism Management plan was also developed to plan for the threat of potential for increasing pressure for access and higher numbers of park visitors since the inscription of the site on the World Heritage list (World Heritage Committee, 2014). Overall, tourism planning is comprehensive and strategic, adopting a market based approach to addressing potential visitor demand. Measures are outlined to ensure the protection of the site’s Outstanding Universal Value (OUV) in the face of rising tourism use (IUCN, 2014).
The “Guidelines for Trekking, Mountaineering and Other Activities in MHRWS” was formulated, and visitation is now permitted within the site, although strictly following the protocols set out in the guidelines. The Guidelines set out the regulations in order to maintain the integrity of the site whilst providing opportunities for the local communities to sustainably earn and continue to steward the MHRWS simultaneously. A Tourism Management plan was also developed to plan for the threat of potential for increasing pressure for access and higher numbers of park visitors since the inscription of the site on the World Heritage list (World Heritage Committee, 2014). Overall, tourism planning is comprehensive and strategic, adopting a market based approach to addressing potential visitor demand. Measures are outlined to ensure the protection of the site’s Outstanding Universal Value (OUV) in the face of rising tourism use (IUCN, 2014).
Sustainable use
The lifestyles and spiritual beliefs of the local and indigenous peoples are based on a healthy respect for the environment and its biodiversity. They have been modified over time to ensure the sustainable use of their resources (State Party of the Philippines, 2014). Some illegal resource use is occurring, however, there appears to be a generally sound collaborative arrangement in place between the authorities and local communities including indigenous groups.
Monitoring
Management authorities have implemented a monitoring and research programme to anticipate climate change effects on the biota and to try to mitigate consequent impacts. Ongoing monitoring of threatened and rare plant and animal species was being carried out on an annual basis (State Party of the Philippines, 2014; World Heritage Committee, 2014). The MHRWS Monitoring & Assessment Programme for Climate Change Adaptation aims to better understand the impacts of climate change on the site’s ecological processes, species and abiotic elements. It represents a well-developed, science based strategy to combat the potentially unknown impacts of climate variability and recognizes the potential for climate change impact on the vertical zonation of the site’s vegetation communities. It also attempts to factor in anticipated impacts from visitation (World Heritage Committee, 2014). However, the level to which the findings of this work are being integrated into management decisions is unclear and there remains limited information on trends of important populations found within the site.
There is a high level of academic interest in the biodiversity contained within the site, as evidenced by recent inventory publications such as Amoroso et al., 2018; Buenavente, 2017; Supsup et al., 2017 and Vidal et al., 2018, however, it is unclear the extent to which this data is integrated into the monitoring activities of the management agencies.
There is a high level of academic interest in the biodiversity contained within the site, as evidenced by recent inventory publications such as Amoroso et al., 2018; Buenavente, 2017; Supsup et al., 2017 and Vidal et al., 2018, however, it is unclear the extent to which this data is integrated into the monitoring activities of the management agencies.
Research
Research projects and studies, particularly on biodiversity assessment and conservation of endangered, endemic and economically important flora and fauna have been undertaken prior to inscription. Local NGOs such as the Philippine Eagle Foundation have been carrying out research work in cooperation with other academic institutions and Government agencies (Bueser et al., 2001; IUCN, 2014; State Party of the Philippines, 2014). There is also ongoing research related the biodiversity values for which the site is listed, including inventories of a number of different taxa found in the site (Amoroso et al., 2018; Amoroso et al., 2019; Buenavente, 2017; Supsup et al., 2017; Vidal et al., 2018; Rosales et al., 2023).
Effectiveness of management system and governance in addressing threats outside the site
The protection of the MHRWS is strengthened by the engagement with and involvement of local and indigenous communities living in its periphery (World Heritage Committee, 2014). The World Heritage site is managed through good cooperative arrangements, which should ensure outside threats do not impinge upon its Outstanding Universal Value (OUV). This collaborative approach has initiated protection and preservation measures and has to date, for example, declined proposals for mining in areas neighboring the site (IUCN, 2014). The work carried out to expand protective legislature against threats from mining in the periphery of the site (IUCN Consultation, 2020a) is also likely to enhance the conservation of the site's OUV in the long term. The lifting of martial law, in place on Mindanao between May 23, 2017 and 31 December, 2019, could have had potential impacts on the OUV of the site, however the precise implications of this remain unclear as does any increase in visitation post the COVID-19 pandemic related travel restrictionsandlikely reduction in visitation.
Effectiveness of management system and governance in addressing threats inside the site
As with threats experienced outside the site, the protection of the MHRWS is strengthened by the engagement with and involvement of local and indigenous communities living in its periphery (World Heritage Committee, 2014). Cooperative arrangements, which support efforts to address threats from outside helps to limit impacts within the site as well, as the threats are largely linked. This collaborative approach has to date, for example, declined proposals for mining in areas neighboring the site (IUCN, 2014), which would increase the overall pressure on the site. The expansion of protective legislature against threats from mining in the periphery of the site (IUCN Consultation, 2020a) is also likely to enhance the conservation of the site's OUV in the long term. Management practices are largely effective although threatened by limited budget and resources.
Staffing and funding for the site remain an issue of some concern. This is especially significant in light of the policy to allow increased visitation within the boundaries of the site. The updated Protected Area Management Plan of MHRWS will need to ensure the integration or mainstreaming and harmonization of all plans and programs of the local government units and other agencies with those of the World Heritage site.
Staffing and funding for the site remain an issue of some concern. This is especially significant in light of the policy to allow increased visitation within the boundaries of the site. The updated Protected Area Management Plan of MHRWS will need to ensure the integration or mainstreaming and harmonization of all plans and programs of the local government units and other agencies with those of the World Heritage site.
The Mount Hamiguitan Protected Area Management Board (PAMB) oversees protection and management of the World Heritage site in accordance with the Mount Hamiguitan Range Wildlife Sanctuary Management Plan. The management plan is due for renewal and efforts should be made to integrate further monitoring of the values of the site into the new plan as it is unclear if the plan has been renewed at this time. The Protected Area Management Office implements the activities in the Plan as well as the policies and directives issued by the PAMB. Together with the “Bantay Gubat” (personnel from the three municipalities with territorial jurisdiction over the site), the PAMO conducts regular monitoring and patrol activities over the core and buffer zones. Previous concerns around sustainable staffing and funding for the site were addressed to some extent by the Expanded National Integrated Protected Area System and associated amendments to national legislation, however, staffing and funding for the site remain an issue of some concern. The MHRWS has experienced periods of strong stakeholder participation, however engagement has diminished over time and it is critical that there is an Indigenous Peoples representative on the PAMB to ensure community participation in decision-making processes.
Critical habitat for a range of plant and animal species within the globally significant Philippine Biodiversity Hotspot
Low Concern
Trend
Stable
Mount Hamiguitan Range Wildlife Sanctuary (MHRWS) remains a critical habitat for a number of species of conservation interest as well as those endemic to the site, the island, and the Philippines. The complete, substantially intact and highly diverse mountain ecosystem and varied habitats within the globally significant biogeographic region of the Philippines represented within the site seem to remain in good condition. However, greater baseline data and monitoring is required in order to establish state and trends in this value. Some additional work has been done on the species found within the site but monitoring over time is needed to evaluate population status as well as identify any impacts from threats to the site and its values, especially those related to climate change. In terms of ferns and lycophytes 152 species, belonging to 27 families and 72 genera have been recorded in the site. The species figure is about 13% of the total number of fern and lycophyte species in the Philippines and nearly 20% of the total number on Mindanao Island. Twelve species are broadly distributed Philippine endemics and three more are found only on Mindanao. Nine species are new records for Mindanao. A site-endemic species, Lindsaea hamiguitanensis, is also documented. Of the 18 threatened species recorded, one is critically endangered, seven are endangered, and 10 are vulnerable (Amoroso et al. 2016). Relox et al. (2010) recorded 140 herptiles belonging to 24 species, of which 15 were reptiles and nine were amphibians. Due to continuing threats, amphibians face immediate extinction trends brought about by human intervention, such as temperature fluctuation and spatiotemporal heterogeneity at all elevations in tropical countries like in the Philippines. Most of these anthropogenic disturbances include habitat destruction, introduced species, pollution, contaminants, pathogens and diseases, and climate change. Meanwhile, land use conversion for agricultural system, which is a common scenario in the lowland forest than in higher elevations, will displace arboreal frogs from their habitats. This has occurred in the marginal areas of the lowland dipterocarp forest on Mt. Hamiguitan. Thus, there is a need for conservation and protection of diverse and endemic herpetofauna and their habitats as they are the most threatened taxa locally and globally (Relox et al. 2010).
Critically endangered trees and plants
Low Concern
Trend
Data Deficient
The MHRWS continues to provide a critical sanctuary to a host of globally threatened and endemic species of flora, of which many are found nowhere else except Mount Hamiguitan. These include critically endangered trees and plants such as Shorea polysperma and Shorea astylosa, and the orchid Paphiopedilum adductum. Overall, the integrity of the forest ecosystem for which the site is inscribed and which contributes significantly to the status of this value, is good. However, further understanding and baseline species data is required to establish comprehensive community dynamics and determine any future trends. Some more recent studies have contributed to establishing a baseline of floristic diversity.
A thorough survey was done from the base to the peak of the mountain Mount Hamiguitan Range Wildlife Sanctuary (MHRWS) to record and identify the
orchid species. MHRWS harbors 45 species of orchids, 23 of them are Philippine endemic, a few may be undescribed. About 53% are epiphytes and 47% are terrestrial. The remarkable richness of orchids found in the present study highlights the importance for conservation of flora in MHRWS and other mountains and forests reserves in Mindanao (Dizon et al. 2018). The number is increasing as new species and varieties continued to be found.
Two recognized species of Aquilaria locally known as “Lapnisan/Laneti” have been reported from Mount Hamiguitan that was subjected to illegal trading, poaching, and overexploitation of the species for high demand of Non-Timber Forest Products (NTFP) in the market. Mount Hamiguitan Range Wildlife Sanctuary (MHRWS) had a higher level of diversity indices with Shannon–Weiner index of Barangay La Union at 2.976 and Barangay Maputi at 2.933. This
could be interpreted to have a moderate floristic diversity value. The primary information on the evaluation of the diversity and population dynamics of Aquilaria and its associated species in Mount Hamiguitan Range Wildlife Sanctuary signify a call for a holistic policy formulation on conservation and preservation of the remaining species in the area (Castaňares et al. 2025).
Mount Hamiguitan Range Wildlife Sanctuary is an important habitat for Zingiberaceae species, however how many are present in the area is still poorly known. Surveys have found that in total, 18 species belonging to eight genera representing three tribes of the family. The most species rich tribe belongs to Alpinieae with 14 species in 6 genera (Naive, 2021).
A thorough survey was done from the base to the peak of the mountain Mount Hamiguitan Range Wildlife Sanctuary (MHRWS) to record and identify the
orchid species. MHRWS harbors 45 species of orchids, 23 of them are Philippine endemic, a few may be undescribed. About 53% are epiphytes and 47% are terrestrial. The remarkable richness of orchids found in the present study highlights the importance for conservation of flora in MHRWS and other mountains and forests reserves in Mindanao (Dizon et al. 2018). The number is increasing as new species and varieties continued to be found.
Two recognized species of Aquilaria locally known as “Lapnisan/Laneti” have been reported from Mount Hamiguitan that was subjected to illegal trading, poaching, and overexploitation of the species for high demand of Non-Timber Forest Products (NTFP) in the market. Mount Hamiguitan Range Wildlife Sanctuary (MHRWS) had a higher level of diversity indices with Shannon–Weiner index of Barangay La Union at 2.976 and Barangay Maputi at 2.933. This
could be interpreted to have a moderate floristic diversity value. The primary information on the evaluation of the diversity and population dynamics of Aquilaria and its associated species in Mount Hamiguitan Range Wildlife Sanctuary signify a call for a holistic policy formulation on conservation and preservation of the remaining species in the area (Castaňares et al. 2025).
Mount Hamiguitan Range Wildlife Sanctuary is an important habitat for Zingiberaceae species, however how many are present in the area is still poorly known. Surveys have found that in total, 18 species belonging to eight genera representing three tribes of the family. The most species rich tribe belongs to Alpinieae with 14 species in 6 genera (Naive, 2021).
Large species diversity and high level of endemism
Good
Trend
Data Deficient
The site continues to harbour a large diversity of plants and animals including large numbers of endemic species, such that the site represents a significant endemism hotspot containing species that exist only in the Philippines, only in Mindanao and only in the World Heritage site. The fragile tropical “bonsai” forest that crowns the Mount Hamiguitan Range Wildlife Sanctuary epitomizes this particular value, and is in overall good condition. However, as with the other values of the site, data is currently lacking to establish any coherent trends in status. Relox et al. (2010) recorded 21 Philippine endemic species of herptiles composed of 14 squamates and seven anurans. The reptilian endemics constituted 93.3% of the total captured species of reptiles in the site.
Most of the herpetofauna surveys conducted in the MHRWS were located in the mountain’s protected areas, which increases conservation as it is protected
against human exploitation. Although there is an increase in the number of herpetofauna species in the mountain, researchers would still agree that the
mountain’s herpetofauna remains poorly understood since a large portion of the forests are still unexplored. The total recorded amphibians and
Reptiles in MHRWS has reached 61 species. In the buffer zone 25 herpetofauna species were documented, accounting for 40% of the total herpetofauna in the mountain (Rosales et al. 2023). An extremely high endemicity has been noted.
Most of the herpetofauna surveys conducted in the MHRWS were located in the mountain’s protected areas, which increases conservation as it is protected
against human exploitation. Although there is an increase in the number of herpetofauna species in the mountain, researchers would still agree that the
mountain’s herpetofauna remains poorly understood since a large portion of the forests are still unexplored. The total recorded amphibians and
Reptiles in MHRWS has reached 61 species. In the buffer zone 25 herpetofauna species were documented, accounting for 40% of the total herpetofauna in the mountain (Rosales et al. 2023). An extremely high endemicity has been noted.
Assessment of the current state and trend of World Heritage values
Data Deficient
Studies and monitoring show that the site is preserved and intact, and new species of fauna and flora continue to be discovered. Baseline data is currently being developed, meaning it is difficult to determine accurate trends at this time. There appear to be few current threats to the site excepting those which emanate from outside the site. In this regard, the increased buffer zone will assist in combating threats and the effective government and community coordination should ensure that surrounding development and activities do not adversely affect the site. The site enjoys multiple levels of legal protection and good planning and programmes have been established to consider the potential impact of tourism and climate change on the site's values. Surveys have been conducted for mammals and amphibians within the buffer zone of the site but further monitoring is needed to identify and trends or changes in the populations. Therefore, trends are unable to be assessed accurately and are data deficient.
Additional information
Water provision (importance for water quantity and quality)
Watersheds of important rivers and creeks are found in MHRWS. Bitaugan, Mabua, Dumagooc/Timbo, Tibanban drain into the Davao Gulf, whilst the Jerico River drains into Pujada Bay. The Salingkomot River empties into the Pacific Ocean. The three rivers: Dumagooc, Tibanban and Bitaugan are the major sources of irrigation water for the lowlands of Governor Generoso and San Isidro (State Party of the Philippines, 2014).
Trends in the impact on the benefits are estimates only given limited baseline and current information is available for the site.
Outdoor recreation and tourism,
Natural beauty and scenery
Health and recreation are important benefits provided by nature and are well recognised as a benefit. Tourism was heavily regulated in the years up until the inscription of the site and remains restricted to some degree. However, the potential for increased tourism has been recognised. In order to establish responsible and sustainable tourism in the site a Visitor and Tourism Management Plan has been developed to ensure sustainable tourism development without negatively impacting the core values of the site (State Party of the Philippines, 2014).
The level of impact on the benefits identified have been estimated but the trend in the impact is difficult to fully assess without further monitoring data on the site and information on species populations.
Sacred natural sites or landscapes,
Cultural identity and sense of belonging
Ancestral Domain Claims (particularly from the Macambol-Mamali United Mandaya Council) include areas inside the Mt. Hamiguitan NR.
Identified threats are mostly from outside the site or within the buffer zone. While the current trend of these threats and their impacts on the benefits of the site are currently unknown, specifically in terms of the impact on cultural benefits of the site they nature of these threats means they are likely to also be impacting on the cultural significance of the site.
There are two main benefits arising from this site; local community engagement and flow on benefits from the development of ecotourism. Local managers continue to work collaboratively with local communities and indigenous peoples on the management of the site and to ensure the equitable access and sharing of benefits, including those that may accrue from tourism. The Visitor and Tourism Plan developed by the State Party aims to deal with a potential increase in tourist numbers without impacting on the OUV of the site (State Party of the Philippines, 2014).
| № | Organization | Brief description of Active Projects | Website |
|---|---|---|---|
| 1 | University of Southern Mindanao in collaboration with Mindanao State University-Iligan Institute of Technology, Southern Christian College, Cebu Biodiversity Conservation Foundation and the National Museum. | Resource Valuation of Hamiguitan Mountain Range conducted in 2008 and 2009 | |
| 2 | Central Mindanao University, Musuan, Bukidnon | Diversity and status of Butterflies across vegetation types of Mt. Hamiguitan, Davao Oriental, Philippines | |
| 3 | Center for Biodiversity Research and Extension in Mindanao (CEBREM), and Department of Biology, Central Mindanao University, University Town, Musuan Bukidnon, Philippines; Department of Biology, Central Mindanao University, University Town Musuan Bukidnon, Philippines; MHRWS-PASO, Department of Environment and Natural Resources, Davao Oriental Province, Philippines; Davao Oriental State College | Status of mammals in the expansion sites of the Mt Hamiguitan Range Wildlife Sanctuary, Mindanao, Philippines. | |
| 4 | Faculty of Agriculture and Life Sciences, Davao Oriental State University | Inventory of Herpetofauna in the Buffer Zone of Mt. Hamiguitan Range Wildlife Sanctuary, San Isidro, Davao Oriental, Philippines |
References
| № | References |
|---|---|
| 1 |
Amoroso, V. B., Coritico, F. P., & Fritsch, P. W. (2016). Species richness and conservation status of ferns and lycophytes in Mt. Hamiguitan Range Wildlife Sanctuary, Davao Oriental, Philippines. Philippine Journal of Science, 145(2), 127-137.
|
| 2 |
Amoroso, V.B., Mohagan, A.B., Coritico, F.P., Lagunday, N.E., Yorong, A.P., Colong, R.D. and Ponce, R.G. (2018). Avifaunal assemblage in the expansion sites of the Mt. Hamiguitan Range Wildlife Sanctuary, Mindanao, Philippines. Nature Conservation Research, 3, pp.103-109.
|
| 3 |
Bueser, G.L., Afan, D.S., Gatil, K.M., Salvador, D.I., Miranda, H.C. JR., Kennedy, R.S., & Grier. J.W. (2001). Distribution and nesting density of Philippine Eagles in Mindanao Island: what we know after 100 years. Ibis, 145,130-145.
|
| 4 |
Castaňares, E., Vedra, S., Perpetua, A., Mazo, K. R., Coronado, W., Bigcas, E., ... & Sumilla, J. (2025, June). Elliptic Fourier Analysis of the two Threatened Aquilaria Lam.(Thymelaeaceae) and its Associated Flora in Mount Hamiguitan Range Wildlife Sanctuary (Mhrws), Davao Oriental, Philippines. In IOP Conference Series: Earth and Environmental Science (Vol. 1506, No. 1, p. 012006). IOP Publishing.
|
| 5 |
Celeste, B. L. (2021). Bantay Gubat’s Challenges in Protecting Mt. Hamiguitan Wildlife Sanctuary, Davao Oriental, Philippines. Journal of Academic Research, 6(1), 11-24.
|
| 6 |
Cereno, D. C., & Roxas, A. T. (2025). Assessment of the institutional arrangements for the Payments for Environmental Services (PES) implementation for watershed conservation: The case of Mount Hamiguitan Range Wildlife Sanctuary (MHRWS). Davao Research Journal, 16(1), 100-120.
|
| 7 |
Dizon, S. A., Ocenar, A. P., & Naïve, M. A. K. (2018). Inventory of orchids in the Mount Hamiguitan Range Wildlife Sanctuary, Davao Oriental, Philippines. Bio Bulletin, 4(1), 37-42.
|
| 8 |
General, D.E.M. and Buenavente, P.A.C. (2017). Checklist of the ants of Mt. Hamiguitan, Mindanao Island, Philippines (Hymenoptera: Formicidae). Halteres, 8, pp.92-102.
|
| 9 |
IUCN (2014). World Heritage Nomination – IUCN Technical Evaluation, Mount Hamiguitan Range Wildlife Sanctuary (The Philippines). In: IUCN World Heritage Evaluations 2014, IUCN Evaluations of nominations of natural and mixed properties to the World Heritage List. WHC/14/38.COM/ [online] Gland, Switzerland: IUCN. Available at: https://whc.unesco.org/en/list/1403/documents/ [Accessed 10 May 2020].
|
| 10 |
IUCN Consultation (2020a). IUCN Confidential Consultation- Mount Hamiguitan Range Wildlife Sanctuary, the Philippines.
|
| 11 |
IUCN Consultation (2020b). IUCN Confidential Consultation- Mount Hamiguitan Range Wildlife Sanctuary, the Philippines.
|
| 12 |
Naive, M. A. K. (2021). An Annotated Checklist of Zingiberaceae Species from Mt. Hamiguitan Range Wildlife Sanctuary, Davao Oriental, Philippines. Journal of Tropical Life Science, 11(1), 101-17.
|
| 13 |
Relox, R. E., Leano, E. P., & Ates-Camino, F. (2011). Herpetofaunal endemism and diversity in tropical forests of Mt. Hamiguitan in the Philippines. Herpetological Conservation and Biology, 6(1), 107-113.
|
| 14 |
Rosales, J. R., Yu, J. A. G., Nanual, B. J., & Ponce, A. G. (2023). Inventory of Herpetofauna in the Buffer Zone of Mt. Hamiguitan Range Wildlife Sanctuary, San Isidro, Davao Oriental, Philippines. Davao Research Journal, 14(2), 50-65.
|
| 15 |
Rosales, J. R., Yu, J. A. G., Nanual, B. J., Ponce, A. G. (2023). Inventory of Herpetofauna in the Buffer Zone of Mt. Hamiguitan Range Wildlife Sanctuary, San Isidro, Davao Oriental, Philippines. Davao Research Journal (DRJ), 14(2), 50-65. https://doi.org/10.59120/drj.v14i2.45
|
| 16 |
State Party of the Philippines (2014). Mount Hamiguitan Range Referral Document. Submitted to the World Heritage Committee at its 38th session (Doha, Qatar, 2014).
|
| 17 |
State Party of the Philippines. (2012). Nomination of Mount Hamiguitan Range Wildlife Sanctuary as a World Heritage Site. Submitted to the World Heritage Committee at its 38th session (Doha, Qatar, 2014) [Accessed 10 May 2020].
|
| 18 |
Supsup, C.E., Guinto, F.M., Redoblado, B.R., Gomez, R.S. (2017). Amphibians and reptiles from the Mt. Hamiguitan Range of eastern Mindanao Island, Philippines: new distribution records. Check List 13(3): 2121, 19 May 2017. https://doi.org/10.15560/13.3.2121
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| 19 |
UNEP-WCMC. (2012). Global Comparative Analysis of Biodiversity Nominations - Mount Hamiguitan Range Wildlife Sanctuary. Cambridge UK: UNEP-WCMC.
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| 20 |
Vidal, K.C., Macusi, E.D. and Ponce, A.G. (2018). Inventory and Morphometrics of Anuran Species Found in Mt. Kilala of the Mt. Hamiguitan Range Wildlife Sanctuary, Governor Generoso, Davao Oriental, Philippines. Philippine Journal of Science, 147(4), pp.629-638.
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| 21 |
World Heritage Committee (2014). Decision 38 COM 8B.8 Mount Hamiguitan Range Wildlife Sanctuary (The Philippines). In: Report of decisions of the 38th session of the World Heritage Committee (Doha, Qatar, 2014). [online] Paris, France: UNESCO World Heritage Centre, Available at: https://whc.unesco.org/en/decisions/6093 [Accessed 10 May 2020].
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| 22 |
World Heritage Committee. (2014). Decision: 38 COM 8B Mount Hamiguitan Range Wildlife Sanctuary Statement of Outstanding Universal Value (The Philippines). In: Decisions Adopted by the World Heritage Committee at its 38th Session (Doha, 2014). [online] Paris, France: UNESCO World Heritage Centre. Available at: http://whc.unesco.org/en/list/1403 [Accessed 11 May 2020].
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