Forestry - IMAGE
|Institution||Utrecht University (UU), Netherlands, https://www.uu.nl/en., PBL Netherlands Environmental Assessment Agency (PBL), Netherlands, https://www.pbl.nl/en.|
|Solution concept||Partial equilibrium (price elastic demand)|
|Anticipation||Simulation modelling framework, without foresight. However, a simplified version of the energy/climate part of the model (called FAIR) can be run prior to running the framework to obtain data for climate policy simulations.|
The forest management module describes regional timber demand and the production of timber in the three different management systems clear felling, selective felling and forest plantations. Deforestation rates reported by FAO are used to calibrate deforestation rates in IMAGE, using a so called additional deforestion.
In IMAGE 3.0, the driver for forest harvest is timber demand per region. Timber demand is the sum of domestic and/or regional demand and timber claims by other regions (export/trade). Production and trade assumptions for saw logs and paper/pulp wood are adopted from external models, such as EFI-GTM 1, and domestic demand for fuelwood is based on the TIMER model. Part of the global energy supply is met by fuelwood and charcoal, in particular in less developed world regions. Not all wood involved is produced from formal forestry activities, as it is also collected from non-forest areas, for example from thinning orchards and along roadsides 23. As few reliable data are available on fuelwood production, own assumptions have been made in IMAGE. While fuelwood production in industrialized regions is dominated by large-scale, commercial operations, in transitional and developing regions smaller proportions of fuelwood volumes are assumed to come from forestry operations: 50% and 32% respectively.
Timber supply & production in forests
In IMAGE, felling in each region follows a stepwise procedure until timber demand is met, attributed to the three aforementioned management systems. The proportion for each management system is derived from forest inventories for different world regions 4 and used as model input. Firstly, timber from forest plantations at the end of their rotation cycle is harvested. Secondly, trees from natural forests are harvested, applying clear felling and/or selective felling. In all management systems, trees can only be harvested when the rotation cycle of forest regrowth has been completed.
Selective logging: Under selective felling, only a regional and time specific fraction of the trees is logged and the other trees remain in the forest. After logging, a fraction of the harvested wood is removed from the forest to fulfil the demand. Biomass left behind in the forest represents losses/residues during tree harvesting (from tree damage and unusable tree parts) or left in the forest because of environmental concerns (biodiversity and nutrient supply). The fraction take-away is derived from literature, defined for industrial roundwood 4. It is further adjusted to account for the demand for wood fuel, for which it equals unity.
Forest plantations: Forest plantations are established for efficient, commercially viable wood production. Their regional establishment in IMAGE 3.0 is scenario driven, based on FAO. The expectation is that increasingly more wood will be produced in plantations because sustainability criteria may limit harvest from natural forests 567. The development of forest plantations in IMAGE and LPJmL is still under development, but expected to be available soon. Forest plantations are assumed to be established firstly on abandoned agricultural land. When sufficient abandoned land is not available, forest plantations are established on cleared forest areas. When a forest plantation has been established, the land cannot be used for other purposes or converted to natural vegetation until the tree rotation cycle has been completed.
Globally, conversion to agricultural land is the major driver of forest clearing, and timber harvest does not result in deforestation, if natural vegetation is regrowing. But there are other causes of deforestation not related to food demand and timber production, such as urbanisation, mining and illegal logging. These activities contribute to loss of forest area, increased degradation risks and a decline in the supply of forest services. To be consistent with the total deforestation rates per world region reported by the FAO 8, IMAGE 3.0 introduces a category additional deforestation. IMAGE assumes no recovery of natural vegetation in these areas, and no agricultural activities.
- Maarit A I Kallio, Alexander Moiseyev, Birger Solberg, others (2004). The global forest sector model EFI-GTM: the model structure. European Forest Institute Joensuu.http://www.efi.int/files/attachments/ www.efi.int/files/attachments/]publications/ir_15.pdf. | |
- FAO (2001). Plantations and wood energy; based on the work of Donald J. Mead (Publication No. Working Paper FP/5) . Rome, Italy: Food and Agriculture Organization of the United Nations. | |
- FAO (2008). Forests and energy key issues.. Rome,Italy: Food and Agriculture Organization of the United Nations. https://openlibrary.org/books/OL22533238M/Forests_and_energy. | |
- E J M M Arets, P J van der Meer, C C Verwer, G M Hengeveld, G W Tolkamp, G J Nabuurs, M van Oorschot (2011). Global wood production: assessment of industrial round wood supply from forest management systems in different global regions (Publication No. Alterra-rapport 1808) .Alterra Wageningen UR. | |
- C Brown (2000). The global outlook for future wood supply from forest plantations (Publication No. GFPOS/WP/03) . Rome: FAO. | |
- J Carle, P Holmgren (2008). Wood from Planted Forests. Forest Products Journal, 58 (12), 6-18. | |
- FAO (2012). FRA 2015, Forest Futures Methodology (Publication No. Forest Resources Assessment Working Paper 182) . Rome, Italy: Food and Agriculture Organization of the United Nations. | |
- FAO (2010). Global Forest Resources Assessment 2010 (Publication No. FAO forestry paper 163) . Rome, Italy: Food and Agriculture Organization of the United Nations. | |