Dynamic Simulation of Tree-Grass Interactions for Global Change Studies

C. Daly, D. Bachelet, J.M. Lenihan, R.P. Neilson, W.J. Parton, D. Ojima

Forestry Sciences Laboratory, 3200 SW Jefferson Way, Corvallis OR 97331 and Natural Resource Ecology Laboratory, Fort Collins CO 80523.

Ecological Applications 10(2):449-469 (2000)

The objective of this study was to dynamically simulate the response of a complex landscape, containing forests, savannas and grasslands to potential climate change. It was thus essential to accurately simulate the competition for light and water between trees and grasses. To accurately represent water competition requires simulating the appropriate vertical root distribution and soil water content. The importance of differential rooting depths in structuring savannas has long been debated. In simulating this complex landscape we examined alternative hypotheses of tree and grass vertical root distribution and their impacts on savanna dynamics under historical and changing climates. MC1, a new dynamic vegetation model, was used to estimate the distribution of vegetation and associated carbon and nutrient fluxes for Wind Cave National Park, SD.

MC1 consists of three linked modules simulating biogeography, biogeochemistry, and fire disturbance. This new tool allows us to document how changes in rooting patterns may affect production, fire frequency and trace gas emissions, and if current vegetation types and lifeform mixtures can be sustained at the same location or replaced by others. Since climate change may intensify resource deficiencies, it will likely affect allocation of resources to roots and their distribution through the soil profile.

By manipulating the rooting depth of two lifeforms -trees and grasses - that are competing for water, and running MC1 for historical climate (1895-1994) and a GCM-simulated future scenario (1995-2094), we document its impact on ecosystem processes and vegetation distribution. Deeply rooting trees causes higher tree productivity, lower grass productivity, and longer fire return intervals. When trees are shallowly rooted, grass productivity exceeds that of trees even if total grass biomass only represents a third to a fourth that of trees. Deeply rooted grasses develop extensive root systems that increase N uptake and the input of litter into soil organic matter pools. Shallowly rooted grasses produce smaller soil carbon pools.

Under the climate change scenario, NPP and live biomass increase for grasses and decrease for trees, and total soil organic matter decreases. However, differences between alternative rooting patterns remain similar. Deeply rooted grasses grow larger than shallowly rooted ones and deeply rooted trees outcompete grasses for resources. Consistent changes in fire frequency and intensity are simulated; more fires occur during the climate change scenario, because temperatures are higher, which results in decreased fuel moisture. Fire also increases in the deeply-rooted grass configurations, because grass biomass, which serves as a fine fuel source, is relatively high.



Figure 1: Simulated total tree (deep rooted) and grass (shallow rooted) biomass (g C m-2) over our study area. 5,000 grid cells were averaged for each year between 1895 until 1994. The date and the extent (number of grid cells that sustained a fire) of simulated natural fires are also presented.