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other starting from year 0. The average C content of the trees included each year is
                 shown in the front most bar representing the landscape level. The losses and gains of C
                 from individual forest stands in the landscape counterbalance and the average C content
                 in the forest is stable over time. (Reprinted with permission from Ref 127. Copyright
                 2011, Peter Eliasson.)

                 Figure 16.9 Development of C stocks and GHG flows over a 240-year period for
                 typical fertilized and unfertilized stands in northern Sweden. The top diagram shows
                 living tree biomass and the bottom diagram shows net substitution benefits of wood
                 product use assuming coal reference fuel, with deductions made for N O, CH , and
                                                                                                2
                                                                                                        4
                 fossil CO  emissions. The dynamics of C in soils and dead biomass (not shown) is
                            2
                 highly influenced by the forest management but occurs at a smaller scale (fluctuations
                                               −1
                 are within 250 ton CO  ha ). A and B denote two possible cases of forest bioenergy
                                          2
                 accounting (see text). (Reprinted with permission from Ref 128. Copyright 2010, IEA
                 Bioenergy.)

                 Figure 16.10 Cumulative CO  emissions and indicative remaining emission space in
                                                  2
                 relation to 2°C target. (Reprinted with permission from Refs 35 and 138. Copyright
                 2011 and 2009, IEA Bioenergy.)

             Chapter 17

                 Figure 17.1 Raw material sources, technical harvesting potentials, and gross potentials
                 of forest chips in Finland and Sweden in 2010.

                 Figure 17.2 Forest fuel supply chain based on comminution at the landing. On the left
                 logging residues from final harvest, truck-mounted chipper. On the right small diameter
                 trees from early thinning, truck-mounted chipper.


                 Figure 17.3 Forest fuel supply chain based on comminution at terminal.
                 Figure 17.4 Forest fuel supply chain based on comminution at power plant.


                 Figure 17.5 Procurement costs (€/m3 solid) of forest chips with different harvesting
                                                           12
                 systems from different raw materials.  The forwarding distance was 250 m and
                 transport distance was 45 km.

             Chapter 18

                 Figure 18.1 Development of the growing stock in Swedish forests from the 1920s up
                 until today. Source: The Swedish National Forest Inventory, Swedish University of
                 Agricultural Sciences, Umeå, Sweden.

                 Figure 18.2 Quick establishment of the new tree crop, proper site preparation, and
                 selection of genetically improved and fast growing tree species are examples of
                 treatments with the potential to reach large areas fast. Thus, they provide the most
                 effective measures to substantially increase future forest production of the slow-moving
                 long-rotation forestry.
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