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Ecoregional Assessment of Biological Diversity in East Kalimantan

Ecoregional Assessment of Biological Diversity in East Kalimantan

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<strong>East</strong> <strong>Kalimantan</strong> <strong>Ecoregional</strong> <strong>Assessment</strong>: Chapter 2 – Target Ecological Systems<br />

hydrological connection; they were probably physically connected <strong>in</strong> the recent past; and<br />

they are vulnerable to similar environmental threats.<br />

Portfolio Design<br />

The goal for <strong>East</strong> <strong>Kalimantan</strong> is 60% <strong>of</strong> all Peat Swamp Forests. The portfolio achieved<br />

65.6% (2% <strong>of</strong> total <strong>in</strong> Stratigraphic Unit 1, 7.25% <strong>in</strong> Unit 2, 44.7% <strong>in</strong> Unit 3, and 10.4% <strong>in</strong><br />

Unit 4). These were distributed to represent their actual proportions <strong>in</strong> each stratigraphic unit<br />

and <strong>in</strong> each annual precipitation zone, if possible.<br />

Results<br />

The distribution <strong>of</strong> Peat Swamp Forest varied greatly <strong>in</strong> each stratigraphic unit, with 65% <strong>of</strong><br />

the areal extent <strong>in</strong> the Prov<strong>in</strong>ce found <strong>in</strong> SU-3. Sixty percent (60%) <strong>of</strong> these swamps also fell<br />

with<strong>in</strong> the <strong>in</strong>termediate precipitation zone (2000 - 3000 mm). The portfolio should then<br />

represent the distributional <strong>in</strong>equity <strong>of</strong> this ecological system type <strong>in</strong> both Stratigraphic Units<br />

and precipitation zones. There was also a significant difference <strong>in</strong> the viability <strong>in</strong>dices for the<br />

occurrences. Those <strong>in</strong> Units 1 and 2 are <strong>in</strong> better condition than those <strong>in</strong> Units 3 and 4.<br />

Swamp Forests were most damaged <strong>in</strong> SU-4 and those <strong>in</strong> SU-3 <strong>of</strong> low viability were<br />

<strong>in</strong>cluded <strong>in</strong> the portfolio because they are considered important for the ecological function <strong>of</strong><br />

the K<strong>in</strong>jau River and the middle Mahakam Lake area. Peat Swamps around the mouth <strong>of</strong> the<br />

Sesayap, Berau and Wa<strong>in</strong> Rivers are also <strong>in</strong>corporated <strong>in</strong>to the portfolio because they form a<br />

broad ecosystem alliance with Mangrove Forests and are ecologically important to the<br />

function <strong>of</strong> these rivers near their deltas, despite their <strong>in</strong>dividually poor viability rank<strong>in</strong>g. The<br />

latter had a generally higher viability <strong>in</strong>dex than those <strong>in</strong> SU-3. Interest<strong>in</strong>gly, there is no Peat<br />

Swamp Forest <strong>in</strong> the immense delta area <strong>of</strong> the Mahakam River, apparently neither extant<br />

nor historic.<br />

The reasons for the low viability <strong>in</strong>dex for the middle Mahakam area occurrences are<br />

discussed <strong>in</strong> the previous Description and Threats sections. However, large tracts <strong>of</strong> Peat<br />

Swamp Forest associated with the K<strong>in</strong>jau River are <strong>in</strong>cluded because <strong>of</strong> the importance <strong>of</strong> the<br />

‘black rivers’ flow<strong>in</strong>g from these forests to native fish and other fluvifauna <strong>in</strong> this area – as<br />

well as their importance to terrestrial fauna and flora, particularly primates. This is also based<br />

upon expert op<strong>in</strong>ion that, if further protected from fire and other human disturbance,<br />

occurrences selected <strong>in</strong> the portfolio could rehabilitate naturally. This is an important po<strong>in</strong>t,<br />

because the matrix lowland ra<strong>in</strong>forests <strong>in</strong> the middle Mahakam area around these Peat<br />

Swamp Forests also have ‘poor’ or ‘very poor’ viability <strong>in</strong>dices. They have been converted<br />

for agricultural purposes or have been burned on multiple occasions and would take a very<br />

long time (>200 years) to recover their natural floristics and structure – if at all. The key to<br />

this possibility is the absolute protection <strong>of</strong> the forests from further disturbances – which <strong>in</strong><br />

this day and age is neither practical nor realistic <strong>in</strong> this particular area.<br />

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