Wehea-Kelay Essential Ecosystem Area: Difference between revisions
No edit summary |
No edit summary |
||
| (2 intermediate revisions by the same user not shown) | |||
| Line 13: | Line 13: | ||
* The main reported threats include the expansion of palm oil plantations and illegal logging activities. | * The main reported threats include the expansion of palm oil plantations and illegal logging activities. | ||
* Conservation efforts have primarily centered on rehabilitating natural habitats, community awareness raising and community led patrols. | * Conservation efforts have primarily centered on rehabilitating natural habitats, community awareness raising and community led patrols. | ||
= Site characteristics = | = Site characteristics = | ||
The Wehea–Kelay Essential Ecosystem Area in East Kalimantan, located between the Regencies of Berau and East Kutai, spans over 530,000 hectares and is home to one of the largest remaining populations of Northeast Bornean orangutans (Atmoko et al. 2021). | The Wehea–Kelay Essential Ecosystem Area in East Kalimantan, located between the Regencies of Berau and East Kutai, spans over 530,000 hectares and is home to one of the largest remaining populations of Northeast Bornean orangutans ([[#R01925|Atmoko et al. 2021]]). | ||
'''Table 1. Basic site information for Wehea-Kelay Essential Ecosystem Area''' | '''Table 1. Basic site information for Wehea-Kelay Essential Ecosystem Area''' | ||
| Line 72: | Line 68: | ||
| | | | ||
| | | | ||
|Atmoko et al. 2021 | |[[#R01925|Atmoko et al. 2021]] | ||
|The paper provides orangutan density estimates as ranges derived from surveys across multiple landscape areas (e.g., PT Gunung Gajah Abadi, PT Karya Lestari, PT Hutan Lindung Wehea). The reported density estimate is the '''mean orangutan density estimate''' was calculated as a weighted average using range midpoints. However, this is an approximation due to insufficient data on the exact area covered by each density class. | |The paper provides orangutan density estimates as ranges derived from surveys across multiple landscape areas (e.g., PT Gunung Gajah Abadi, PT Karya Lestari, PT Hutan Lindung Wehea). The reported density estimate is the '''mean orangutan density estimate''' was calculated as a weighted average using range midpoints. However, this is an approximation due to insufficient data on the exact area covered by each density class. | ||
| | | | ||
| Line 85: | Line 81: | ||
| | | | ||
| | | | ||
|Atmoko et al. 2021 | |[[#R01925|Atmoko et al. 2021]] | ||
|According to the 2016 Population and Habitat Viability Assessment (PHVA), the estimated population of orangutans in the Wehea-Kelay Landscape ranges from 806 to 821 individuals (Atmoko et al. 2021). | |According to the 2016 Population and Habitat Viability Assessment (PHVA), the estimated population of orangutans in the Wehea-Kelay Landscape ranges from 806 to 821 individuals (Atmoko et al. 2021). | ||
| | | | ||
| Line 106: | Line 102: | ||
|2.1.3 Industrial farming (including palm oil) | |2.1.3 Industrial farming (including palm oil) | ||
|Present (unknown severity) | |Present (unknown severity) | ||
|The expansion of oil palm plantations is reported as a threat and poses long-term risks to forest integrity (Atmoko et al. 2021). | |The expansion of oil palm plantations is reported as a threat and poses long-term risks to forest integrity ([[#R01925|Atmoko et al. 2021]]). | ||
|Ongoing (2021) | |Ongoing (2021) | ||
|- | |- | ||
| Line 112: | Line 108: | ||
|5.3.2 Commercial logging | |5.3.2 Commercial logging | ||
|Present (unknown severity) | |Present (unknown severity) | ||
|Illegal logging activities have been reported, and a 2021 multi-stakeholder gap analysis revealed that some logging concession management units have not implemented orangutan protection programs (Atmoko et al. 2021). | |Illegal logging activities have been reported, and a 2021 multi-stakeholder gap analysis revealed that some logging concession management units have not implemented orangutan protection programs ([[#R01925|Atmoko et al. 2021]]). | ||
|Ongoing (2021) | |Ongoing (2021) | ||
|} | |} | ||
| Line 131: | Line 127: | ||
|2 Counter-wildlife crime | |2 Counter-wildlife crime | ||
|2.12 Implement community control of patrolling, banning hunting and removing snares | |2.12 Implement community control of patrolling, banning hunting and removing snares | ||
|Patrol teams like Petkuq Mehuey involve Dayak youth in biodiversity monitoring, fire prevention, and enforcing no-logging zones in critical wildlife areas (Atmoko et al. 2021). | |Patrol teams like Petkuq Mehuey involve Dayak youth in biodiversity monitoring, fire prevention, and enforcing no-logging zones in critical wildlife areas ([[#R01925|Atmoko et al. 2021]]). | ||
|Wehea Nehes Liah Bing traditional institution | |Wehea Nehes Liah Bing traditional institution | ||
|Ongoing (2021) | |Ongoing (2021) | ||
| Line 137: | Line 133: | ||
|5 Protection & restoration | |5 Protection & restoration | ||
|5.6 Habitat restoration | |5.6 Habitat restoration | ||
|Habitat management activities were reported to be present (Sherman et al. 2022). | |Habitat management activities were reported to be present ([[#R01926|Sherman et al. 2022]]). | ||
| | | | ||
|2001-Ongoing (2022) | |2001-Ongoing (2022) | ||
| Line 143: | Line 139: | ||
|4 Education & awareness | |4 Education & awareness | ||
|Other | |Other | ||
|Community outreach and capacity building (Sherman et al. 2022). | |Community outreach and capacity building ([[#R01926|Sherman et al. 2022]]). | ||
| | | | ||
|2001-Ongoing (2022) | |2001-Ongoing (2022) | ||
| Line 159: | Line 155: | ||
= Research activities = | = Research activities = | ||
Research activities have been reported present in Wehea-Kelay Essential Ecosystem Area (Sherman et al. 2022). | Research activities have been reported present in Wehea-Kelay Essential Ecosystem Area ([[#R01926|Sherman et al. 2022]]). | ||
= Documented behaviours = | = Documented behaviours = | ||
| Line 175: | Line 171: | ||
= References = | = References = | ||
<span id="R01925"></span>Atmoko, T., Sudiono, E., Rifqi, M. A., & Dharma, A. P. (2021). The best practices of endangered wildlife habitat management on landscape scale: A lesson from the Wehea–Kelay essential ecosystem areas. Yayasan Konservasi Alam Nusantara. https://www.researchgate.net/publication/379024604 | |||
Atmoko, T., Sudiono, E., Rifqi, M. A., & Dharma, A. P. (2021). The best practices of endangered wildlife habitat management on landscape scale: A lesson from the Wehea–Kelay essential ecosystem areas. Yayasan Konservasi Alam Nusantara. https://www.researchgate.net/publication/379024604 | |||
<span id="R01926"></span>Sherman, J., Voigt, M., Ancrenaz, M., Wich, S. A., Qomariah, I. N., Lyman, E., …, & Meijaard, E. (2022). Orangutan killing and trade in Indonesia: Wildlife crime, enforcement, and deterrence patterns. ''Biological Conservation'', 276, 109744. [https://doi.org/10.1016/j.biocon.2022.109744 doi:10.1016/j.biocon.2022.109744] | |||
'''Page created by: '''Aime Mizero''' Date:''' 2025-05-30 | '''Page created by: '''Aime Mizero''' Date:''' 2025-05-30 | ||
Latest revision as of 16:31, 12 October 2026
Asia > Indonesia > Wehea-Kelay Essential Ecosystem Area
Français | Português | Español | Bahasa Indonesia | Melayu
Summary
- Northeast Bornean orangutans (Pongo pygmaeus morio) are present in Wehea-Kelay Essential Ecosystem Area.
- The orangutan population size ranges from 806 to 821 individuals, from 2016 survey.
- The orangutan population trend is unknown.
- The site has a total size of 5,321.43 km².
- The main reported threats include the expansion of palm oil plantations and illegal logging activities.
- Conservation efforts have primarily centered on rehabilitating natural habitats, community awareness raising and community led patrols.
Site characteristics
The Wehea–Kelay Essential Ecosystem Area in East Kalimantan, located between the Regencies of Berau and East Kutai, spans over 530,000 hectares and is home to one of the largest remaining populations of Northeast Bornean orangutans (Atmoko et al. 2021).
Table 1. Basic site information for Wehea-Kelay Essential Ecosystem Area
| Species | Pongo pygmaeus morio |
| Area | 5,321.43 km² |
| Coordinates | Lat: 1.664757 , Lon: 116.674340 |
| Type of site | Non-protected area (Essential ecosystem area) |
| Habitat types | Subtropical/tropical moist lowland forest |
| Type of governance |
Types of sites Governance types Habitat types
Ape status
Table 2. Ape population estimates reported for Wehea-Kelay Essential Ecosystem Area
| Species | Year | Occurrence | Encounter or vistation rate (nests/km; ind/day) | Density estimate [ind./ km²] (95% CI) | Abundance estimate (95% CI) | Survey area | Sampling method | Analytical framework | Source | Comments | A.P.E.S. database ID |
|---|---|---|---|---|---|---|---|---|---|---|---|
| Pongo pygmaeus morio | 2017-2018 | 0.57 | Wehea-Kelay Essential Ecosystem Area | Atmoko et al. 2021 | The paper provides orangutan density estimates as ranges derived from surveys across multiple landscape areas (e.g., PT Gunung Gajah Abadi, PT Karya Lestari, PT Hutan Lindung Wehea). The reported density estimate is the mean orangutan density estimate was calculated as a weighted average using range midpoints. However, this is an approximation due to insufficient data on the exact area covered by each density class. | ||||||
| Pongo pygmaeus morio | 2016 | Wehea-Kelay Essential Ecosystem Area | Atmoko et al. 2021 | According to the 2016 Population and Habitat Viability Assessment (PHVA), the estimated population of orangutans in the Wehea-Kelay Landscape ranges from 806 to 821 individuals (Atmoko et al. 2021). |
Sampling methods Analytical frameworks
Threats
Table 3. Threats to apes reported for Wehea-Kelay Essential Ecosystem Area
| Category | Specific threats | Threat level | Description | Year of threat |
|---|---|---|---|---|
| 2 Agriculture & aquaculture | 2.1.3 Industrial farming (including palm oil) | Present (unknown severity) | The expansion of oil palm plantations is reported as a threat and poses long-term risks to forest integrity (Atmoko et al. 2021). | Ongoing (2021) |
| 5 Biological resource use | 5.3.2 Commercial logging | Present (unknown severity) | Illegal logging activities have been reported, and a 2021 multi-stakeholder gap analysis revealed that some logging concession management units have not implemented orangutan protection programs (Atmoko et al. 2021). | Ongoing (2021) |
Conservation activities
Table 4. Conservation activities reported for Wehea-Kelay Essential Ecosystem Area
| Category | Specific activity | Description | Implementing organization(s) | Year of activity |
|---|---|---|---|---|
| 2 Counter-wildlife crime | 2.12 Implement community control of patrolling, banning hunting and removing snares | Patrol teams like Petkuq Mehuey involve Dayak youth in biodiversity monitoring, fire prevention, and enforcing no-logging zones in critical wildlife areas (Atmoko et al. 2021). | Wehea Nehes Liah Bing traditional institution | Ongoing (2021) |
| 5 Protection & restoration | 5.6 Habitat restoration | Habitat management activities were reported to be present (Sherman et al. 2022). | 2001-Ongoing (2022) | |
| 4 Education & awareness | Other | Community outreach and capacity building (Sherman et al. 2022). | 2001-Ongoing (2022) |
Challenges
Enablers
Research activities
Research activities have been reported present in Wehea-Kelay Essential Ecosystem Area (Sherman et al. 2022).
Documented behaviours
Exposure to climate change impacts
External links
References
Atmoko, T., Sudiono, E., Rifqi, M. A., & Dharma, A. P. (2021). The best practices of endangered wildlife habitat management on landscape scale: A lesson from the Wehea–Kelay essential ecosystem areas. Yayasan Konservasi Alam Nusantara. https://www.researchgate.net/publication/379024604
Sherman, J., Voigt, M., Ancrenaz, M., Wich, S. A., Qomariah, I. N., Lyman, E., …, & Meijaard, E. (2022). Orangutan killing and trade in Indonesia: Wildlife crime, enforcement, and deterrence patterns. Biological Conservation, 276, 109744. doi:10.1016/j.biocon.2022.109744
Page created by: Aime Mizero Date: 2025-05-30