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I N T E G R A T E D S I N K E N H A N C E M E N T A S S E S S M E N T INSEA PARTNERS Forest production and carbon storage -potentials of European forestry.

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Presentation on theme: "I N T E G R A T E D S I N K E N H A N C E M E N T A S S E S S M E N T INSEA PARTNERS Forest production and carbon storage -potentials of European forestry."— Presentation transcript:

1 I N T E G R A T E D S I N K E N H A N C E M E N T A S S E S S M E N T INSEA PARTNERS Forest production and carbon storage -potentials of European forestry FORESTRY MODELLING Oskar Franklin Elena Moltchanova Michael Obersteiner Florian Kraxner Rupert Seidl (BOKU, Wien) Manfred J Lexer (BOKU, Wien) Dimitry Rokityanskiy Kentaro Aoki Ian McCallum Dagmar Schwab Glen Armstrong Forestry Program

2 Ϊ Ϊ Ϊ Ϊ Ϊ I N S E A Overview Aims and framework Forest model (the OSKAR model) Results for different scenarios Conclusions and implications

3 Ϊ Ϊ Ϊ Ϊ Ϊ I N S E A Forests and management

4 Ϊ Ϊ Ϊ Ϊ Ϊ I N S E A FASOM OSKAR forestry model the OSKAR Forestry model and data

5 Ϊ Ϊ Ϊ Ϊ Ϊ I N S E A Forestry modeling framework Forestry output: C storage (soil, biomass) Wood Energy biom. Forested area Potentials: C storage Wood Energy biom. management scenarios: (harvest, thinning, species) climate change effect Initial state forest and soil climate FASOM model -economic optimization of land use OSKAR model -forestry scenarios NPP model management costs prices alternative land uses

6 Ϊ Ϊ Ϊ Ϊ Ϊ I N S E A Forest growth modeling

7 Ϊ Ϊ Ϊ Ϊ Ϊ I N S E A Tree growth Productivity of the site (NPP) controls growth rate and equilibrium biomass

8 Ϊ Ϊ Ϊ Ϊ Ϊ I N S E A Self-thinning and mortality Growth and competition causes self-thinning The number of trees per are is limited by the self thinning line. This number decreases with increasing tree size N trees/area stand biomass self-thinning limit

9 Ϊ Ϊ Ϊ Ϊ Ϊ I N S E A Forest management “And see this ring right here, Jimmy?... That’s another time the old fellow miraculously survived some big forest fire.”

10 Ϊ Ϊ Ϊ Ϊ Ϊ I N S E A Thinning management Thinning purposes: get larger trees (but fewer) harvest more take out bad trees facilitate regeneration Growth effect: reduced density but more resources available per tree Mortality effect: reduced self-thinning mortality relative density self-thinning stand growth relative density

11 Ϊ Ϊ Ϊ Ϊ Ϊ I N S E A Thinning scenarios Thinning at an early stage have a small effect on final biomass After thinning at a late stage, the old trees does fill up the space Large thinnings leaves space and resources (light) for new generation Thinnings can result in larger total harvests (thinnings + final harvest) stem biomass 20% 70% 0% time biomass + acc. thinnings

12 Ϊ Ϊ Ϊ Ϊ Ϊ I N S E A Other management options Rotation length Species selection Fertilization

13 Ϊ Ϊ Ϊ Ϊ Ϊ I N S E A Validation of the model Production estimate agrees well with a detailed tree level physiological model PICUS (hybrid –patch model) Thinning effect is almost identical in both models stem volume (m 3 /ha) red thin line: OSKAR blue thick line: PICUS number of trees per ha years

14 Ϊ Ϊ Ϊ Ϊ Ϊ I N S E A Model summary Predicts carbon accumulation, forestry production and management costs in response to management (thinning, species selection, rotation) and climate change In contrast to most existing management models, it does not rely on local empirical relations and local site indexes, but is based on globally applicable biophysical principles and species characteristics. it can be run for any region and time period and is easily integrated with global models of climate change effects (LPJ) and land use economic optimization models (FASOM model), which is done in the European carbon sink project INSEA.

15 Ϊ Ϊ Ϊ Ϊ Ϊ I N S E A Reality and results

16 Ϊ Ϊ Ϊ Ϊ Ϊ I N S E A Current and future forests modeled biomass and estimated by FAO for EU countries, for 2005 and mean of 2005-2100 for two scenarios: 1) all managed, 2) old forest protected *old forests: 7.1 % of total forest area on average GHG emission EU 25

17 Ϊ Ϊ Ϊ Ϊ Ϊ I N S E A Current and future forests Total maximum sustainable harvests in EU ≈ 200 MtC/year (2005-2100)

18 Ϊ Ϊ Ϊ Ϊ Ϊ I N S E A Forest development scenarios dead wood biomass

19 Ϊ Ϊ Ϊ Ϊ Ϊ I N S E A Forest development scenarios

20 Ϊ Ϊ Ϊ Ϊ Ϊ I N S E A Forest development scenarios

21 Ϊ Ϊ Ϊ Ϊ Ϊ I N S E A Forest development scenarios dead wood biomass

22 Ϊ Ϊ Ϊ Ϊ Ϊ I N S E A Forest development scenarios

23 Ϊ Ϊ Ϊ Ϊ Ϊ I N S E A Forest development scenarios dead wood biomass

24 Ϊ Ϊ Ϊ Ϊ Ϊ I N S E A Forest development scenarios

25 Ϊ Ϊ Ϊ Ϊ Ϊ I N S E A Conclusions Future forest prediction strongly depends on estimates of current forests. There is a potential to increase harvests substantially in about 20 years from now Increasing the rotation time/age at harvest is a way to increase the carbon storage in the forest, but initially reduces harvest. By protecting old forests, carbon storage can be increase about 20% almost without reduction in harvests


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