Difference between revisions of "Ulu Segama-Malua"

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Latest revision as of 05:23, 23 February 2022

Asia > Malaysia > Ulu Segama-Malua

Summary[edit]

  • 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[edit]

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 4.956727, 117.878134
Designation Unclassified
Habitat types Subtropical/tropical moist lowland forest, Subtropical/Tropical Heavily Degraded Former Forest

IUCN habitat categories Site designations

Ape status[edit]

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[edit]

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

IUCN Threats list

Conservation activities[edit]

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[edit]

Table 5. Challenges reported for Ulu Segama-Malua

Challenge Source
Not reported

Research activities[edit]

Documented behaviours[edit]

Table 6. Ape behaviors reported for Ulu Segama-Malua

Behavior Source
Not reported

External links[edit]

Ulu Segama Malua - Sabah Forestry Department

Relevant datasets[edit]

A.P.E.S Portal

References[edit]

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