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A Supplemental HCVF Assessment on the Sumatran Tiger ...

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FINAL REPORT <strong>Tiger</strong> <str<strong>on</strong>g>HCVF</str<strong>on</strong>g> <str<strong>on</strong>g>Supplemental</str<strong>on</strong>g> <str<strong>on</strong>g>Assessment</str<strong>on</strong>g> – Serapung FMU<br />

2.3 Ecology of Peat Swamp Forests around <strong>the</strong> FMU<br />

The SmartWood <str<strong>on</strong>g>HCVF</str<strong>on</strong>g> report describes in detail <strong>the</strong> ecological characteristics and<br />

associated flora and fauna of <strong>the</strong> major habitat types found in <strong>the</strong> Siak-Pelalawan<br />

block. Five habitats are recognised in this landscape - tall PSF, mixed PSF, short PSF,<br />

sec<strong>on</strong>dary habitats, and mangrove/coastal habitats. Only short PSF was found to be<br />

absent from <strong>the</strong> FMU.<br />

Coastal peat-swamp forest, where peat accumulates <strong>on</strong> top of marine sediments<br />

(Reiley, Ahmad-Shah & Brady 1996), is predominant within <strong>the</strong> FMU – presenting as<br />

Tall PSF across <strong>the</strong> majority of <strong>the</strong> FMU area. The FMU PSF abuts tidal rivers and<br />

coastline, providing an accumulati<strong>on</strong> of freshwater in <strong>the</strong> peat soil which maintains<br />

sufficient hydrostatic pressure to repel tidal saltwater incursi<strong>on</strong>s into <strong>the</strong> inland soil<br />

profile.<br />

Relatively little terrestrial wildlife research has been carried out within PSF ecotypes in<br />

general, with most previous PSF wildlife studies limited to investigati<strong>on</strong> of arboreal and<br />

aquatic animal species. This lack of ecological c<strong>on</strong>text has presented a challenge to<br />

<strong>the</strong> interpretati<strong>on</strong> of results obtained during this assessment.<br />

Despite this paucity of data regarding terrestrial animals, some inferences can be made<br />

from general ecological studies within <strong>the</strong> PSF ecosystem. Low nutrient levels of soils<br />

in mature PSF almost certainly limit primary producti<strong>on</strong>. In such a habitat plants are<br />

expected to defend <strong>the</strong>ir leaves and o<strong>the</strong>r edible parts as fiercely as possible against<br />

potential herbivores (Whitten et al. 2000). C<strong>on</strong>sistent with low productivity ecosystems,<br />

a number of studies have indicated that <strong>the</strong> density of primates is lower in PSF than in<br />

dry lowland systems (Galdikas 1978, Marsh and Wils<strong>on</strong> 1981, Mackinn<strong>on</strong> 1983) which<br />

decreases fur<strong>the</strong>r still with increasing distance from rivers (MacKinn<strong>on</strong> et al. 1996).<br />

Many species of mammals and birds inhabiting PSF are <strong>the</strong> same as those in o<strong>the</strong>r<br />

lowland tropical rainforest (Medway 1977, Davies and Payne 1982; MacKinn<strong>on</strong> 1983;<br />

Wells 1985) although, for at least terrestrial mammals, <strong>the</strong>se are found to live at much<br />

lower densities in PSF (Mert<strong>on</strong> 1962, Janzen 1974). Extrapolated to <strong>the</strong> typical prey<br />

species of <strong>the</strong> tiger, PSF would be expected to have a lower carrying capacity and<br />

hence its habitat potential for tigers would be less optimal when compared to o<strong>the</strong>r<br />

lowland forest ecotypes.<br />

O<strong>the</strong>r research has suggested that PSF has ecological attributes that increase its<br />

c<strong>on</strong>servati<strong>on</strong> value. While PSF is generally c<strong>on</strong>sidered to have a relatively low floristic<br />

diversity (MacKinn<strong>on</strong> et al. 1996), recent studies have shown that tree diversity can be<br />

comparable to, and sometimes even greater than, that of forests <strong>on</strong> mineral soils<br />

(Hanum & Leprun 1999). PSF also provides a habitat for a number of endemic and rare<br />

tree species (Ibrahim 1997).<br />

Similarly, of <strong>the</strong> 57 mammal and 237 bird species recorded in PSF of peninsular<br />

Malaysia, 51% and 27% respectively are listed as globally threatened species<br />

(Sebastian 2002). In Sumatra, PSF c<strong>on</strong>stitutes <strong>the</strong> largest remaining area of low-level<br />

forest habitat and, as such, now represents a vital refuge for not <strong>on</strong>ly peat swamp<br />

specialists, but also a wider range of lowland specialist species (Sebastian 2002).<br />

2.3.1 Habitat Modificati<strong>on</strong> of Peat Swamp Forest by Logging<br />

The Siak-Pelalawan forest block represents a modified PSF ecosystem due to<br />

logging activities. The entire forest block has, in <strong>the</strong> recent past, been managed<br />

and exploited under HPH logging c<strong>on</strong>cessi<strong>on</strong>s (Figure 4). Inspecti<strong>on</strong> of satellite<br />

imagery (Landsat 2001, 2002 and SPOT 2004) reveals logging rails have been<br />

used widely across <strong>the</strong> forest block, and that severe degradati<strong>on</strong> of forest is<br />

associated with <strong>the</strong> more accessible areas.<br />

<strong>Sumatran</strong> <strong>Tiger</strong> C<strong>on</strong>servati<strong>on</strong> Program Pg 13/68

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