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FOREST RESOURCES TREND AND SUSTAINABLE FOREST MANAGEMENT IN PENINSULAR MALAYSIA<br />

The classification of the above functional classes is by no means exclusive. An area of the<br />

PRF can be classified under more than one functional class provided their uses are not<br />

contradictory. For example, forest trekking, camping, picnicking and bird watching activities<br />

should not pose problems in the catchment areas provided these are done in low densities.<br />

There is a need to formulate specific management practices for each of the functional classes.<br />

One of the aims of classifying the forest into different functions is to ensure that the forest is<br />

used and managed within its capacity. Over-use and inappropriate management result in forest<br />

health degradation that could change the forest ecosystem. The drastic changes in the ecosystem<br />

will negatively impact human welfare, health and food production.<br />

Selective Management System (SMS)<br />

Currently, the production forests are managed under Selective Management System. The system<br />

advocates the selection of a cutting regime based on diameter limits and species composition<br />

of the standing trees. In Peninsular Malaysia, the implementation of the SMS involves<br />

conducting forest activities that could be distinctly categorized into three stages, namely preharvesting,<br />

during harvesting and post-harvesting activities. The pre-harvesting activities<br />

include pre-felling forest inventory, cutting limit prescription and timber tagging. During<br />

harvesting, activities include directional felling and forest road construction while post harvest<br />

activities include forest survey, post-felling forest inventory and prescription of silvicultural<br />

treatments. Some of the activities are further elaborated below.<br />

The SMS is designed to achieve sustainability of the forest with management objectives of<br />

economic and efficient harvesting under prevailing conditions. It requires the selection of<br />

management (cutting) regimes based on inventory data, which will be equitable to logger and<br />

forest owner, as well as ensuring ecological balance and environmental quality.<br />

Pre-Harvesting Activities<br />

Cutting Limits Prescription<br />

The cutting limits prescription is based on the stand and stock information obtained from the<br />

pre-felling forest inventory, together with other relevant information needed to determine the<br />

optimal cutting regimes (diameter limits) for the forest area. Under SMS, the next cut is expected<br />

to be between 30-55 years and with an estimated net economic outturn of 30–40 cubic meters<br />

per hectare. The criteria for cutting limits prescription are as follows:<br />

• The cutting limit prescribed for the group of dipterocarp species should not be less than<br />

50 cm dbh, except for Neobalanocarpus heimii (Chengal) where the cutting limit prescribed<br />

should not be less than 60 cm dbh.<br />

• The cutting limit prescribed for the group of non-dipterocarp species should not be less<br />

than 45 cm dbh.<br />

• The residual stocking should have at least 32 sound commercial trees per ha from the<br />

diameter class 30–45 cm or its equivalence.<br />

• The difference in the cutting limits prescribed between the dipterocarp and that of the<br />

non-dipterocarp species should be at least 5 cm.<br />

• The percentage of dipterocarp species in the residual stand for trees having 30 cm dbh<br />

and above should not be less than that in the original stand.<br />

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