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ateam - Potsdam Institute for Climate Impact Research

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ATEAM final report Section 5 and 6 (2001-2004) 28<br />

the end of the series. In some cases, the values of different series converge. In the case of Pinus<br />

pinaster, the series corresponding to climate change become lower than the baseline at the end of the<br />

simulation. The lowest values <strong>for</strong> this variable are found in Pinus halepensis simulations. Thus, in spite<br />

of the overall positive effects of climate change on wood production some species will be affected<br />

negatively, especially in the longer term in the Mediterranean. In Mediterranean and Southern regions<br />

the conditions of increasing temperature and, in certain areas, a decrease of precipitation determines a<br />

generalized decrease of the soil water available especially marked in southern zones of Europe. This is<br />

accompanied by an increase of the evapotranspiration processes (water use). In fact, simulations <strong>for</strong><br />

specific species indicate that in some regions tree mortality may go up as an effect of this climate<br />

change. This effect was mainly simulated in Southern regions where <strong>for</strong>ests are at the edge of their biogeographical<br />

distribution.<br />

Important research challenges to further explore potential impacts on tree growth in the Mediterranean<br />

and the rest of Europe are to better introduce interactions between direct effects of atmospheric carbon<br />

dioxide concentrations and other environmental constraints, as well as the interactions with soil<br />

processes and the flow of nutrients.<br />

Two papers from this work are underway in the Proceedings of the Spanish Association <strong>for</strong> Forestry<br />

Sciences Cuadernos de la Sociedad Española de Ciencias Forestales (see Annex 2).<br />

6.2.2.3 Carbon Storage<br />

European terrestrial carbon balance<br />

Principal investigators: M.T. Sykes, P. Morales, B. Smith (Department of Physical Geography &<br />

Ecosystems Analysis, Lund University), I.C. Prentice (Department of Earth Sciences, University of<br />

Bristol), J. House (Max Planck <strong>Institute</strong> <strong>for</strong> Biogeochemistry), W. Cramer, A. Bondeau, S. Sitch, S.<br />

Zaehle, D. Schröter, Fred Hattermann, Jürgen Kropp (<strong>Potsdam</strong> <strong>Institute</strong> <strong>for</strong> <strong>Climate</strong> <strong>Impact</strong> <strong>Research</strong>,<br />

PIK).<br />

The Kyoto Protocol specified legally binding commitments by most industrialized countries to reduce<br />

their collective greenhouse gas (GHG) emissions. With the goal of reaching these targets at the lowest<br />

possible cost, the protocol created two flexibility mechanisms, GHG emissions trading and the Clean<br />

Development Mechanism (CDM). Important CDM strategies are carbon dioxide emission reduction by<br />

using alternative energy sources (e.g. hydropower and biomass), as well as by maintaining important<br />

carbon sinks like soil organic matter and <strong>for</strong>ests. Within this political framework, net terrestrial carbon<br />

storage becomes an ecosystem service. In<strong>for</strong>mation on European carbon storage is useful to politicians<br />

in negotiations regarding the Kyoto process. Additionally, a range of stakeholders are interested in<br />

estimates of net carbon storage potential of their land. Depending on European Union (EU) mitigation<br />

policies, owners or managers of land may receive credits <strong>for</strong> land use and management that maintains<br />

or increases carbon storage.<br />

Throughout the project we have collaborated with stakeholders interested in carbon storage, which<br />

included representatives of national and European <strong>for</strong>est owners, land owners, agricultural producers,<br />

paper industry, consultancy groups to the paper industry, farm management agencies, consultancy<br />

groups to environmental engineers, environmental finance companies, national and European<br />

representatives of environmental agencies, as well as biomass energy companies and foundations (see<br />

section Stakeholder Dialogue). These stakeholders expressed an interest in the carbon storage<br />

potential of <strong>for</strong>ests. Besides the direct commercial interest in carbon storage, stakeholders also<br />

mentioned the potential side effects of increasing the carbon storage in terrestrial biomass, such as<br />

enhanced recreational value of a landscape and possible positive impacts on water purification.<br />

The ecosystem service carbon storage is indicated by the variable net biome exchange (NBE), which is<br />

provided by the dynamic global vegetation model LPJ (Sitch et al. 2003). The NBE of an area is<br />

determined by net primary production (NPP, net carbon uptake by the plants), and carbon losses due to<br />

soil heterotrophic respiration, fire, harvesting, and land use change. Net carbon storage is the integral of

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