gcb12156-sup-0002-AppendixS1_model

advertisement
Supporting Material
Appendix S1: Details of models used.
LPJ-GUESS
LPJ-GUESS is a generalized, process-based model of vegetation dynamics and
biogeochemistry that includes a representation of tree population dynamics based on simulating
age cohorts of tree species (Gerten et al., 2004, Sitch et al., 2003, Smith et al., 2001). The
model aims to capture physiological processes (e.g. photosynthesis, plant respiration, and
microbial decomposition) and associated fluxes of carbon and water between soil layers,
vegetation, and the atmosphere, which are simulated on a daily time step. Growth and vegetation
dynamics are updated annually by allocating net primary production (NPP) to leaves, sapwood,
and fine roots, and by simulating sapwood-to-heartwood conversion, litterfall, fine root turnover,
establishment, and mortality (Sitch et al., 2003). The model is driven by daily temperature,
precipitation, and percentage sunshine hours, and atmospheric CO2 concentration. We used the
species-specific tree parameterization developed by Hickler et al. (2012) that includes the main
European tree, shrub and grass species. The different species are characterized by specific
establishment, growth, mortality and metabolic rates, and bioclimatic limits determining their
distribution range (Sitch et al., 2003, Smith et al., 2001). The LPJ model framework has been
successfully used to simulate vegetation cover and carbon and water fluxes at a number of
European locations (Hickler et al., 2012, Rammig et al., 2010), and has previously been applied
to central European alpine sites (Manusch et al., 2012, Portner et al., 2010, Wolf et al., 2012).
To account for the stochastic nature of tree establishment and mortality we simulated 200
replicates of each vegetation patch, with projected vegetation at each patch taken as the mean of
these replicates. Forest management was approximated according to site- specific management
regimes (see main text). During forest management tree boles were removed while all leaves
and roots, and 5% of trees’ sapwood and heartwood, was added to the litter pool.
ForClim
ForClim (v3.0) is a climate-sensitive forest “gap” model, developed to simulate forest
stand dynamics over a wide range of environmental conditions (Bugmann & Cramer, 1998,
Bugmann, 1996). ForClim simulates the establishment, growth and mortality of trees on
multiple forest patches to derive stand properties at a spatial extent of ca. 15-20 ha by averaging
the properties simulated at the patch scale. Tree establishment and growth are regulated by
growing degree-days, light availability, and soil moisture and nitrogen status. The model is
driven by mean monthly temperatures and the monthly precipitation sums (Bugmann &
Solomon, 2000). Tree growth (i.e. DBH increment) is modelled using an empirical growth
equation (cf. Moore, 1989) that incorporates species-specific constraints on maximum growth
rate and maximum tree height (Rasche et al., 2012). From diameter at breast height, allometric
equations are used to estimate other tree characteristics as well as total aboveground biomass
(Bugmann, 1994). The model is currently parameterized for 31 European tree species, and has
been widely tested for the representation of forest dynamics in the northern temperate zone of
three continents (Bugmann, 2001, Bugmann & Cramer, 1998, Bugmann & Solomon, 2000,
Didion et al., 2011, Rasche et al., 2012, Shao et al., 2001). Within ForClim a wide range of
silvicultural treatments can be simulated (Rasche et al., 2011).
LandClim
LandClim is a spatially explicit forest landscape model that incorporates competitiondriven forest dynamics, climate effects, and forest disturbances to simulate forest dynamics on a
landscape scale (Elkin et al., 2012, Schumacher & Bugmann, 2006, Schumacher et al., 2004,
Schumacher et al., 2006). LandClim simulates forest growth in 625 m2 cells using simplified
versions of tree recruitment, growth and competition derived from ForClim. Forest growth is
determined by climatic parameters (monthly temperature and precipitation), soil properties and
topography, and the spatially explicit processes of seed dispersal, landscape disturbances such as
fire and windthrow, and forest management that link individual cells.. Forest succession
processes within each cell are simulated on a yearly time step, while landscape-level processes
are simulated on a decadal time step. The model has been used in the Central Alps, North
American Rocky Mountains, and Mediterranean forests, to simulate current forest (Schumacher
et al. 2006) as well as paleo-ecological (Colombaroli et al., 2010, Henne et al., 2011) and future
forest dynamics (Schumacher & Bugmann, 2006, Temperli et al., 2012). The simulation of
forest management is spatially explicit such that dynamic interactions between management and
landscape heterogeneity are captured (Temperli et al., 2012).
Appendix S1 References
Bugmann H (1994) Functional types of trees in temperate and boreal forests: Classification and
testing. In: GCTE Workshop on Plant Functional Types and Climatic Change. pp Page,
Potsdam, Germany.
Bugmann H (2001) A comparative analysis of forest dynamics in the Swiss Alps and the
Colorado Front Range. Forest Ecology and Management, 145, 43-55.
Bugmann H, Cramer W (1998) Improving the behaviour of forest gap models along drought
gradients. Forest Ecology and Management, 103, 247-263.
Bugmann HKM (1996) A simplified forest model to study species composition along climate
gradients. Ecology, 77, 2055-2074.
Bugmann HKM, Solomon AM (2000) Explaining forest composition and biomass across
multiple biogeographical regions. Ecological Applications, 10, 95-114.
Colombaroli D, Henne PD, Kaltenrieder P, Gobet E, Tinner W (2010) Species responses to fire,
climate and human impact at tree line in the Alps as evidenced by palaeo-environmental
records and a dynamic simulation model. Journal of Ecology, 98, 1346-1357.
Didion M, Kupferschmid AD, Wolf A, Bugmann H (2011) Ungulate herbivory modifies the
effects of climate change on mountain forests. Climatic Change, 109, 647-669.
Elkin C, Reineking B, Bigler C, Bugmann H (2012) Do small-grain processes matter for
landscape scale questions? Sensitivity of a forest landscape model to the formulation of
tree growth rate. Landscape Ecology, 27, 697-711.
Gerten D, Schaphoff S, Haberlandt U, Lucht W, Sitch S (2004) Terrestrial vegetation and water
balance - hydrological evaluation of a dynamic global vegetation model. Journal of
Hydrology, 286, 249-270.
Henne PD, Elkin CM, Reineking B, Bugmann H, Tinner W (2011) Did soil development limit
spruce (Picea abies) expansion in the Central Alps during the Holocene? Testing a
palaeobotanical hypothesis with a dynamic landscape model. Journal of Biogeography,
no-no.
Hickler T, Vohland K, Feehan J et al. (2012) Projecting the future distribution of European
potential natural vegetation zones with a generalized, tree species-based dynamic
vegetation model. Global Ecology and Biogeography, 21, 50-63.
Manusch C, Bugmann H, Heiri C, Wolf A (2012) Tree mortality in dynamic vegetation models A key feature for accurately simulating forest properties. Ecological Modelling, 243, 101111.
Moore AD (1989) ON THE MAXIMUM GROWTH EQUATION USED IN FOREST GAP
SIMULATION-MODELS. Ecological Modelling, 45, 63-67.
Portner H, Bugmann H, Wolf A (2010) Temperature response functions introduce high
uncertainty in modelled carbon stocks in cold temperature regimes. Biogeosciences, 7,
3669-3684.
Rammig A, Jonsson AM, Hickler T, Smith B, Barring L, Sykes MT (2010) Impacts of changing
frost regimes on Swedish forests: Incorporating cold hardiness in a regional ecosystem
model. Ecological Modelling, 221, 303-313.
Rasche L, Fahse L, Zingg A, Bugmann H (2011) Getting a virtual forester fit for the challenge of
climatic change. Journal of Applied Ecology, 48, 1174-1186.
Rasche L, Fahse L, Zingg A, Bugmann H (2012) Enhancing gap model accuracy by modeling
dynamic height growth and dynamic maximum tree height. Ecological Modelling, 232,
133-143.
Schumacher S, Bugmann H (2006) The relative importance of climatic effects, wildfires and
management for future forest landscape dynamics in the Swiss Alps. Global Change
Biology, 12, 1435-1450.
Schumacher S, Bugmann H, Mladenoff DJ (2004) Improving the formulation of tree growth and
succession in a spatially explicit landscape model. Ecological Modelling, 180, 175-194.
Schumacher S, Reineking B, Sibold J, Bugmann H (2006) Modeling the impact of climate and
vegetation on fire regimes in mountain landscapes. Landscape Ecology, 21, 539-554.
Shao GF, Bugmann H, Yan XD (2001) A comparative analysis of the structure and behavior of
three gap models at sites in northeastern China. Climatic Change, 51, 389-413.
Sitch S, Smith B, Prentice IC et al. (2003) Evaluation of ecosystem dynamics, plant geography
and terrestrial carbon cycling in the LPJ dynamic global vegetation model. Global
Change Biology, 9, 161-185.
Smith B, Prentice IC, Sykes MT (2001) Representation of vegetation dynamics in the modelling
of terrestrial ecosystems: comparing two contrasting approaches within European climate
space. Global Ecology and Biogeography, 10, 621-637.
Temperli C, Bugmann HKM, Elkin C (2012) Adaptive management for competing forest goods
and services under climate change. Ecological Applications.
Wolf A, Lazzarotto P, Bugmann H (2012) The relative importance of land use and climatic
change in Alpine catchments. Climatic Change, 111, 279-300.
Download