PROFESSOR DEREK EAMUS, University of Technology Sydney
Trees are important components of landscapes, whether that is in an urban, rural or wilderness landscapes. Their importance includes their economic, biodiversity, conservation, ecological, aesthetic and spiritual value. Although their economic value as sources of timber is well understood, their broader economic value through provision of ecosystem services remains poorly recognized (Eamus et al. 2005). Examples of ecosystem services that are provided by trees, woodlands and forests include stabilization of soil through their root system, absorption of carbon dioxide in the mitigation of climate change, transpiration of water to offset flooding and salinity risks and the cooling effects of canopies of trees in urban landscapes.
Carbon uptake is required for tree growth, and even mature, non-growing trees absorb carbon dioxide each day. The process of carbon uptake during photosynthesis is always associated with transpirational water loss from leaves and an understanding of how these two processes respond to changes in the environment is central to understanding how trees may respond to climate change.
The aim of this presentation is to present daily and seasonal patterns of carbon and water fluxes of some native woodland trees and then to discuss how climate change may impact on these processes.
Two methods of measuring tree water use and canopy water and carbon fluxes were used. In the first, sapflow sensors (Fig. 1a) were used to measure the rate of flow of water up the stem of individual trees. In the second, eddy covariance methods were used (Fig. 1b). Descriptions of these methods can be found in Eamus et al. (2006). The data presented in this talk are derived from studies undertaken in the Northern Territory of Australia.
RESULTS AND DISCUSSION
Rainfall in the NT is highly seasonal, with a pronounced wet season (November to March inclusive) when 90% of annual rainfall occurs (Fig. 2). In contrast, the daily potential rate of evaporation is relatively constant, varying between about 5 and 7.5 mm per day (Fig. 2). Because of the seasonality of rainfall, soil moisture content in the upper soil profile remains high in the wet season but declines in the dry season (Fig. 3). The cause of this decline is uptake of water by tree roots, surface evaporation and deep drainage which occurs early in the dry season.
The decline in soil moisture content of the upper 50 cm of soil, where most of the roots are located, is reflected in the change in pre-dawn leaf water potential (Fig. 4). Declines in pre-dawn water potential (moving away from zero to a more negative value) are indicative of declining soil water availability and reveal the development of increasing levels of water stress in the leaves as the dry season progresses.
It is interesting to compare the behaviour of two contrasting ecosystems, a eucalypt open forest (EOF) and a monsoon forest (MSF) in their response to the cessation of rains that occurs at the end of the wet season (Fig. 4). The decline in water potential of the eucalypt forest is much larger than that of the MSF because the MSF is found at low points in the landscape where surface and sub-surface run-on of water keeps the soil wet all year. This difference in behaviour is also reflected in the difference in response of the leaf area index of the two ecosystems (Fig. 5). Leaf area index is a measure of how much leaf is present in the canopy and it varies seasonally. As soil moisture content declines for long periods (weeks and months) leaf fall occurs and the leaf index of the canopy falls significantly in the eucalypt canopy.
The two dominant species growing in the northern savannas around Darwin in the NT are Eucalyptus tetrodonta and E. miniata. These two species are evergreen and transpire all year. In some years, such as 1998, transpiration rates may be reduced in the dry season, but most often, there is no decline in transpiration observed between the wet season and dry season, as observed in 1999 (Fig. 6). This lack of seasonality in water use in the dry season has been observed across many years and is counter-intuitive. It occurs because of the ability of these evergreen trees to extract water from deep stores in the soil. These species extract water from up to 8 m depth. Despite the evergreen trees showing a reasonably constant rate of transpiration between the wet and dry seasons, (averaged over many years) there is a highly consistent and large decline in the rate of carbon uptake by savannas in the dry season (Fig. 7). This is the result of three factors. First, the annual C4 grasses that have a very high leaf area index in the wet season, die in the first month of the dry season and stop fixing carbon. Second, the deciduous trees lose their leaves in the first month of the dry season. Consequently, the amount of green leaf that is fixing carbon in the dry season is much less than that seen in the wet season. Finally, as the dry season progresses, the soil moisture content declines and there is some closure of stomata even in the evergreen trees. This further reduces the ability of the savanna ecosystem to fix carbon, as shown in Fig. 7.
The importance of soil moisture and atmospheric water content (RH) to the behaviour of leaf physiology is highlighted in Figure 8. This figure shows how these two factors combine to reduce stomatal conductance and hence water loss and carbon uptake. This pattern of responses is observed almost universally across all trees of Australia, whether they are growing in urban, rural or wilderness landscapes.
Predicting the effect of climate change on water and carbon fluxes presents many challenges. A large experiment being conducted in NSW by a consortium of UWS, UTS, UNSW and NSW Primary Industries is growing 12 trees from seedling to 6 y age under CO2 enriched conditions with two levels of water supply. The aim of this work is to validate a process based model of tree growth and function under future climate scenarios. At the moment it is likely that the increase in carbon dioxide concentration within the atmosphere is already having an impact on the amount of carbon being taken up by Australian landscapes into vegetation. The reduction in stomatal conductance that invariably arises in response to an increase in atmospheric CO2 concentration in broadleaved species increases water-use-efficiency and this, coupled to the increased C uptake, may be causing significant increases in tree cover in native woodlands of Australia. The biggest unknown at the moment is the impact of climate change on the fire regime of Australia. Changes in fire frequency, fire intensity and the timing of fires, is likely to have a major impact on the native vegetation of Australia.
- Eamus, D., Hutley, L. and O’Grady, A.P 2001. Carbon and water fluxes above a north Australian savanna. Tree Physiology, 21, 977-988.
- Eamus, D., Macinnins-Ng, C., Hose, G.C., Zeppel, M.J., Taylor, D.T., and Murray, B. 2005. In the service of ecosystem services. Turner Review for the Australian Journal of Botany 53, 1-19.
- Eamus, D., Hatton, T., Cook, PG and Colvin, C (2006). Ecohydrology: vegetation function, water and resource management. Pp348. CSIRO Press, Melbourne.
- Hutley, L., Eamus, D., and O’Grady 2000. Evapotranspiration from Eucalypt open-forest savanna of northern Australia. Functional Ecology 14, 183-194.
- Kelly, G. (2005) Tree water use and soil water dynamics in savannas of northern Australia. PhD thesis, Charles Darwin University.
- Kelley, G., Eamus, D., O’Grady A., and Hutley, L. (2007). A comparison of tree water use in two contiguous vegetation communities of the seasonally dry tropics of north Australia: the importance of site water budget to tree hydraulics. Australian Journal of Botany. In Press.