Prioritization of Target Areas for Rehabilitation: A Case Study from West Kalimantan, Indonesia

To rehabilitate degraded forestlands and conserve the remaining forests in Kalimantan, effective measures are needed that accommodate various land uses in the landscape. We present a pragmatic model for prioritizing target areas for rehabilitation and discuss a potential approach, combining traditional reforestation and the forest management methods of local Dayak tribes with the operations of a commercial tree plantation venture, to promote the rehabilitation of elements of the tropical lowland rainforest. We characterized the vegetation and land use in the study area and assume that rehabilitation and conservation value will be maximized by concentrating rehabilitation efforts around forest patches with high cultural and economic value to the local Dayaks. We simulated potential enlargement of these culturally important forests and built a model to calculate a rehabilitation value for each forest fragment and fragment group with easily measurable criteria of vegetation and area. The model gives priority to areas where large continuous areas of culturally important forests already exist and/or will be created. The individual culturally important forest patches and their total area in the landscape are small, but even a small potential enlargement may be enough to establish relatively large concentrations. The potential matrix area for rehabilitation is dominated by young successional woody vegetation. Forested areas, although heavily degraded, connect several culturally important forest concentrations and are the most desirable target for rehabilitation. A well-managed commercial tree plantation can enhance conditions for the protection and rehabilitation of degraded forestlands through traditional reforestation and forest management methods.

[1]  K. F. Wiersum,et al.  Forest gardens as an ‘intermediate’ land-use system in the nature–culture continuum: Characteristics and future potential , 2004, Agroforestry Systems.

[2]  H. Tan,et al.  A Century of Plant Species Loss from an Isolated Fragment of Lowland Tropical Rain Forest , 1996 .

[3]  W. Jong,et al.  The impact of rubber on the forest landscape in Borneo , 2001 .

[4]  B. Palik,et al.  USING LANDSCAPE HIERARCHIES TO GUIDE RESTORATION OF DISTURBED ECOSYSTEMS , 2000 .

[5]  G. Ådjers,et al.  Population dynamics of tree seedlings in a mixed dipterocarp rainforest before and after logging and crown liberation , 1996 .

[6]  Christopher M. U. Neale,et al.  Identifying Sites for Riparian Wetland Restoration: Application of a Model to the Upper Arkansas River Basin , 1997 .

[7]  K. Ruokolainen,et al.  The role of traditional forest gardens in the conservation of tree species in West Kalimantan, Indonesia , 2003, Biodiversity & Conservation.

[8]  K. Brown Addressing Trade-Offs in Forest Landscape Restoration , 2005 .

[9]  L. Fahrig,et al.  Mosaic Landscapes and Ecological Processes , 1995, Springer Netherlands.

[10]  W. Jong,et al.  Developing swidden agriculture and the threat of biodiversity loss , 1997 .

[11]  E. Wollenberg,et al.  Local Participation, Livelihood Needs, and Institutional Arrangements: Three Keys to Sustainable Rehabilitation of Degraded Tropical Forest Lands , 2005 .

[12]  M. Dove Smallholder rubber and swidden agriculture in Borneo: A sustainable adaptation to the ecology and economy of the tropical forest , 1993, Economic Botany.

[13]  A. Gkaraveli,et al.  Determining priority areas for native woodland expansion and restoration in Snowdonia National Park, Wales , 2004 .

[14]  Leighton,et al.  Impact of El Nino and logging on canopy tree recruitment in borneo , 1999, Science.

[15]  R. Otsamo Secondary forest regeneration under fast-growing forest plantations on degraded Imperata cylindrica grasslands , 2004, New Forests.

[16]  P. Virtanen The Role of Customary Institutions in the Conservation of Biodiversity: Sacred Forests in Mozambique , 2002, Environmental Values.

[17]  Lauri Vesa,et al.  Enrichment planting of dipterocarps in logged-over secondary forests: effect of width, direction and maintenance method of planting line on selected Shorea species , 1995 .

[18]  R. Otsamo,et al.  CHANGES AND ALTERNATIVES IN FARMERS' LIVELIHOOD PLANNING IN AN INDUSTRIAL FOREST PLANTATION AREA IN WEST KALIMANTAN, INDONESIA , 2002 .

[19]  Panayotis Dimopoulos,et al.  Evaluation and mapping of the conservation significance of habitats using GIS: an example from Crete, Greece , 2004 .

[20]  The Role of Commercial Plantations in Forest Landscape Restoration , 2005 .

[21]  N. Dudley,et al.  Negotiations and Conflict Management , 2005 .

[22]  D. Peart,et al.  Availability and extraction of forest products in managed and primary forest around a Dayak village in West Kalimantan, Indonesia , 1995 .

[23]  Lauri Vesa,et al.  Growth of dipterocarp seedlings in artificial gaps : an experiment in a logged-over rainforest in South Kalimantan, Indonesia , 1996 .

[24]  N. Salafsky Forest gardens in the Gunung Palung region of West Kalimantan, Indonesia. Defining a locally-developed, market-oriented agroforestry system , 1994 .

[25]  D. Fuller,et al.  Loss of Forest Cover in Kalimantan, Indonesia, Since the 1997–1998 El Niño , 2004 .

[26]  Thoams F. Allnutt Mapping and Modelling as Tools to Set Targets, Identify Opportunities, and Measure Progress , 2005 .

[27]  R. Otsamo,et al.  Indigenous livelihood systems in industrial tree-plantation areas in West Kalimantan, Indonesia: Economics and plant-species richness , 2003, Agroforestry Systems.

[28]  Kendra Cipollini,et al.  Planning for Restoration: A Decision Analysis Approach to Prioritization , 2005 .

[29]  G. Ådjers,et al.  Effect of gap liberation on the performance and growth of dipterocarp trees in a logged-over rainforest , 1997 .