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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 />

• Fire<br />

Due to the fewer roads present <strong>in</strong> this forest system type, because <strong>of</strong> the legal logg<strong>in</strong>g<br />

restrictions, fire tends to occur less frequently than <strong>in</strong> the lower elevation forests. But<br />

contiguity <strong>of</strong> this forest type with adjacent more heavily used systems, such as lowland<br />

ra<strong>in</strong>forest and karst forest, the danger <strong>of</strong> wildfire spread persists. Impacts are particularly<br />

damag<strong>in</strong>g <strong>in</strong> the montane systems because <strong>of</strong> their removal <strong>of</strong> multiple-layers <strong>of</strong><br />

vegetative habitat features – that is, the bole climbers, v<strong>in</strong>es, ferns, tree orchids, mosses<br />

and fungi present at every level <strong>of</strong> the forest canopy. Each <strong>of</strong> these habitat features serves<br />

as home to numerous, and probably as yet undocumented endemic species <strong>of</strong><br />

<strong>in</strong>vertebrates and small vertebrates.<br />

• Alang alang (Imperata cyl<strong>in</strong>drica) spread.<br />

Recently <strong>in</strong> <strong>East</strong> <strong>Kalimantan</strong>, Alang-alang grasslands have extended widely <strong>in</strong>to Lowland<br />

Ra<strong>in</strong>forest areas. Alang-alang is a fire disclimax species, which prevents natural<br />

rehabilitation <strong>of</strong> disturbed forest. It ma<strong>in</strong>ly results from conversion <strong>of</strong> forests to kebun<br />

(garden plots) on <strong>in</strong>fertile soils and not from slash and burn (swidden) agriculture widely<br />

practiced by traditional people (Kiyono and Hastaniah 2000). The lack <strong>of</strong> regulations to<br />

prevent clear<strong>in</strong>g for one crop rotation, after which land is permanently abandoned, is a<br />

major factor <strong>in</strong> the spread <strong>of</strong> Alang-alang grassland and the permanent conversion <strong>of</strong><br />

Lowland Ra<strong>in</strong>forests. Such a source <strong>of</strong> <strong>in</strong>vasive species may br<strong>in</strong>g it <strong>in</strong>to the Lower<br />

Montane region when or if this forest type beg<strong>in</strong>s to suffer substantially from<br />

deforestation <strong>in</strong> the eventuality that the lowland forests are depleted.<br />

• Swidden agriculture.<br />

MacK<strong>in</strong>non et al. (1996) regard traditional swidden farm<strong>in</strong>g as caus<strong>in</strong>g little damage to<br />

the environment. Fallow land from swidden farm<strong>in</strong>g usually becomes secondary forest,<br />

and ultimately develops <strong>in</strong>to mixed dipterocarp forest after a fallow period longer than 70<br />

years, if the seeds <strong>of</strong> primary forest species are provided by reta<strong>in</strong><strong>in</strong>g nearby<br />

reproductive-aged stand<strong>in</strong>g forest (Okimori and Matius 2000). However, new<br />

technologies, <strong>in</strong>creased population pressure and the need for traditional farmers to plant<br />

cash crops have dramatically altered traditional swidden practices and telescoped the<br />

fallow period (Jessup and Vayda 1988). There is a need to identify areas <strong>of</strong> Lower<br />

Montane/Middle Montane Ra<strong>in</strong>forest where traditional swidden practices can be<br />

ma<strong>in</strong>ta<strong>in</strong>ed and to discourage other farm<strong>in</strong>g techniques that are <strong>in</strong>imical to ma<strong>in</strong>tenance<br />

<strong>of</strong> forest structure and floristics.<br />

• Lack <strong>of</strong> Strict Enforcement <strong>of</strong> Government Regulations.<br />

There are exist<strong>in</strong>g regulations that forbid logg<strong>in</strong>g on slopes greater than 45% or above<br />

600 m a.s.l. (Keputasan Presiden No.48/1983). These regulations should be strictly<br />

enforced because illegal logg<strong>in</strong>g <strong>in</strong> these and other areas is rampant. Logg<strong>in</strong>g on high<br />

slopes is particularly damag<strong>in</strong>g, as most <strong>of</strong> these areas are prone to erosion if they are<br />

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