Ulu Segama-Malua
Asia > Malaysia > Ulu Segama-Malua
Summary
- Northeast Bornean orangutans (Pongo pygmaeus morio) are present in the Ulu Segama-Malua landscape.
- It has been estimated that 2,580 (CI: 1,295-5,866) individuals occur in the site.
- The orangutan population trend is unknown.
- The site has a total size of 2,400 km².
- Key threats to orangutans include logging, forest degradation and fragmentation.
- Conservation activities have focused on habitat restoration.
Site characteristics
The Ulu Segama-Malua (USM) landscape is located in the Malaysian state of Sabah between 116°28′E and 4°14′N and comprises approximately 240,000 hectares of lowland forest (WWF 2020, Ancrenaz et al. 2010). The site sustains one of the largest orangutan populations in Sabah (WWF 2020). To the north of USM, Bukit Piton Forest Reserve (12,000 ha) is found, which is an area of high conservation value (WWF 2020). The USM landscape consists of a variably steep terrain, with many hills and ridges, although Malua's topography is predominantly flat and low (Ancrenaz et al. 2010).
Table 1. Basic site information for Ulu Segama-Malua
Area | 2,400 km² |
Coordinates | |
Designation | Unclassified |
Habitat types | Subtropical/tropical moist lowland forest, Subtropical/Tropical Heavily Degraded Former Forest |
IUCN habitat categories Site designations
Ape status
Surveys in 2002 and 2007 show that orangutan populations can be maintained in forests that have been lightly and sustainably logged (Ancrenaz et al. 2010). However, in heavily logged forests there was a decline in orangutan numbers (Ancrenaz et al. 2010). Nest distribution in the forests of Ulu Segama Malua indicates that orangutans leave areas undergoing active disturbance, reaching forests that are located up to 500 meters above sea level (Ancrenaz et al. 2010).
Table 2. Ape population estimates in Ulu Segama-Malua
Species | Year | Abundance estimate (95% CI) | Density estimate [ind./ km²] (95% CI) | Encounter rate (nests/km) | Area | Method | Source | Comments | A.P.E.S. database ID |
---|---|---|---|---|---|---|---|---|---|
Pongo pygmaeus morio | 2002 | 4,584 (2,064-11,064) | Segama forests | Aerial survey | Ancrenaz et al. 2005 | ||||
Pongo pygmaeus morio | 2007 | 1.52 (0.5-4.1) | North Ulu Segama | Aerial survey | Ancrenaz et al. 2010 | ||||
Pongo pygmaeus morio | 2007 | 0.13 (0.04-0.39) | Segama East | Aerial survey | Ancrenaz et al. 2010 | ||||
Pongo pygmaeus morio | 2007 | 0.79 (0.29-2.16) | Segama Central | Aerial survey | Ancrenaz et al. 2010 | ||||
Pongo pygmaeus morio | 2007 | 1.76 (0.64-4.80) | Segama South West | Aerial survey | Ancrenaz et al. 2010 | ||||
Pongo pygmaeus morio | 2007 | 1.64 (0.58-4.52) | Malua | Aerial survey | Ancrenaz et al. 2010 | ||||
Pongo pygmaeus morio | 2007 | 2,580 (1,295-5,866) | USM forests, total | Aerial and ground survey | Ancrenaz et al. 2010 |
Threats
Surveys in 2002 and 2007 show that orangutan populations can be maintained in forests that have been lightly and sustainably logged (Ancrenaz et al. 2010). However, in heavily logged forests there was a decline in orangutan numbers (Ancrenaz et al. 2010). Nest distribution in the forests of Ulu Segama Malua indicates that orangutans leave areas undergoing active disturbance, reaching forests that are located up to 500 meters above sea level (Ancrenaz et al. 2010).
Table 3. Threats to apes in Ulu Segama-Malua
Category | Specific threats | Threat level | Quantified severity | Description | Year of threat |
---|---|---|---|---|---|
1. Residential & commercial development | Unknown | ||||
2. Agriculture & aquaculture | 2.1 Annual & perennial non-timber crops | High | Oil palm plantations surround the landscape, especially along the eastern and northern borders (Ancrenaz et al. 2010, WWF 2020). | Ongoing (2020) | |
3. Energy production & mining | Unknown | ||||
4. Transportation & service corridors | 4.1 Roads & railroads | High | 5.5 roads/km of transect in overdegraded forest; 3.4 roads/km of transect in degraded forest (Ancrenaz et al. 2010). | Logging roads that are present in higher frequency in overdegraded forests (Ancrenaz et al. 2010). | Ongoing (2010) |
5. Biological resource use | 5.3 Logging & wood harvesting | High | Heavy logging has led to decreased orangutan abundance at the site, as well as forest fragmentation (Ancrenaz et al 2010). | Ongoing (2010) | |
6. Human intrusion & disturbance | Unknown | ||||
7. Natural system modifications | 7.1 Fire & fire suppression | Present, but threat severity unknown | Fires to clear land, but also due to severe droughts (Ancrenaz et al. 2010). | Ongoing (2010) | |
8. Invasive & other problematic species, genes, diseases | Unknown | ||||
9. Pollution | Unknown | ||||
10. Geological Events | Absent | ||||
11. Climate change & severe weather | Unknown | ||||
12. Other options | Absent |
Conservation activities
Conventional logging practices and heavy extraction rates, coupled with high road densities and indiscriminate felling, has resulted in a mosaic of highly degraded forests bordering hilltops and isolated patches of moderate habitat; in other words, habitat in the USM landscape is very heterogeneous (Ancrenaz et al. 2010). Multiple logging cycles that began in 1957 and ended in 2007 led to drastic alterations in the original forest structure and integrity (Ancrenaz et al. 2010). Forest fragmentation has forced the orangutan population to spread into less suitable habitats (Ancrenaz et al. 2010).
Table 4. Conservation activities in Ulu Segama-Malua
Category | Specific activity | Description | Year of activity |
---|---|---|---|
1. Residential & commercial development | Not reported | ||
2. Agriculture & aquaculture | Not reported | ||
3. Energy production & mining | Not reported | ||
4. Transportation & service corridors | Not reported | ||
5. Biological resource use | Not reported | ||
6. Human intrusion & disturbance | Not reported | ||
7. Natural system modifications | Not reported | ||
8. Invasive & other problematic species, genes, diseases | Not reported | ||
9. Pollution | Not reported | ||
10. Education & Awareness | Not reported | ||
11. Habitat Protection | 11.7. Restore habitat corridors | Restoration in the Bukit Piton forest is intended to have a positive impact on the rest of the landscape by connecting key patches of forest (WWF 2020). | Ongoing (2020) |
12. Species Management | Not reported | ||
13. Livelihood; Economic & Other Incentives | Not reported |
Conservation activities list (Junker et al. 2017)
Challenges
Table 5. Challenges reported for Ulu Segama-Malua
Challenge | Source |
---|---|
Not reported |
Research activities
Documented behaviours
Table 6. Ape behaviors reported for Ulu Segama-Malua
Behavior | Source |
---|---|
Not reported |
External links
Ulu Segama Malua - Sabah Forestry Department
Relevant datasets
References
Ancrenaz, M., Ambu, L., Sunjoto, I., Ahmad, E., Manokaran, K., Meijaard, E., & Lackman, I. (2010). Recent surveys in the forests of Ulu Segama Malua, Sabah, Malaysia, show that orang-utans (P. p. morio) can be maintained in slightly logged forests. PLoS One, 5(7), e11510.
Ancrenaz, M., Gimenez, O., Ambu, L., Ancrenaz, K., Andau, P., Goossens, B., ... & Lackman-Ancrenaz, I. (2005). Aerial surveys give new estimates for orangutans in Sabah, Malaysia. PLoS Biology, 3(1), e3.
WWF (2020). Lessons Learnt from 12 Years Restoring the Orangutan’s Habitat: the Bukit Piton Forest Reserve in the Malaysian State of Sabah. Online: https://wwf.panda.org/wwf_news/?364737/WWF-field-series-Lessons-learnt-from-restoring-the-orangutan-habitat-in-the-Malaysian-State-of-Sabah
Page completed by: A.P.E.S. Wiki team Date: 16/11/2021