2-15: Vegetation Responses to a Changing Environment
Eugene S. Takle
© 1997
(Click here if you
want the unit combined with images.)
Much of this information has been taken from:
Watson, Robert T., Marufu C. Zinyowera, Richard H. Moss, 1996: Climate
Change 1995, Impacts Adaptations and Mitigation of Climate Change:
Scientific-Technical Analyses. Cambridge University Press. 879 pp.
The lecture on plant physiological effects of a changing
environment addresses the impact of various influences, particularly
climate change, on an individual plant. In this lecture we overview some
of the interrelations among plants in plant communities and ecosystems and
how they might be affected by climate change.
Some Definitions
Introduction
All living organisms in terrestrial ecosystems ultimately depend
directly or indirectly on photosynthesis for their energy requirements. To
review the essentials of the photosynthesis process, check the source on
"how plants make food" We will explore some climatic driving forces for ecosystem
processes and then examine some ecological processes on various scales,
including the global where we consider the global production of plant
carbon.
Climatic Driving Forces
Solar radiation, temperature, precipitation, air humidity, and
atmospheric CO2 are the key ambient forces that drive ecosystem processes.
Of these, temperature, water availability, and CO2 levels are
subject to change in the next 100 years.
Impact of Temperature Change on Plant Growth and Ecosystems
Plant growth and health may benefit from increased temperatures of
global warming in that some regions will experience reduced incidence of
damage from freezing and chilling. Plants in other regions may suffer from
stress due to elevated temperatures. There is some evidence that extreme
events (droughts, floods, high winds, etc.) may accompany global warming,
in which case plants may experience isolated highly damaging events.
NPP will generally be increased by moderate increases in
temperature estimated to occur in the next 60 years, especially in boreal
and mid-latitude regions. Estimates are that NPP will increase 1% per 1
degree C in regions where the mean annual temperature is 30 C and 10% in
regions where the mean annual temperature is 0 C. Crop yield will be
discussed in a future lecture, but the result is that the regions of
reduced yields are reasonably balanced by regions of yield gain.
Impact of Precipitation and Water Availability
Plant leaves have small openings called stomata that can be
adjusted to regulate the exchange of water vapor and CO2 with the
atmosphere. Plants not under water stress keep their stomata open for
optimum CO2 exchange. Under stress, however, plants close their stomata to
restrict water loss. They also may allow their leaves to droop to reduce
light absorption or they may shed leaves to reduce water loss. C4 plants
have higher WUE than C3 plants. Higher atmospheric CO2 levels will cause
stomata to close slightly, increase WUE, and increase carbon gain for
plants with limited water supply. Higher temperatures may lead to higher
differences in water-vapor concentration inside and outside the stomata,
however, and thereby lead to reduced WUE.
Direct Effects of CO2 Concentration
Photosynthetic rates in C3 plants increase by 25-75% for a doubling
of CO2. For C4 plants the data are less conclusive and range from no
response to an increase of 10-25%. Results likely are temperature
dependent. Increases in CO2, with accompanying increases photosynthetic
rate and decreased water requirement, translate into increased growth and
crop yield in C3 plants, increased growth in C4 plants, and increased tree
seedling growth. The response to elevated CO2 will be most pronounced in
regions where water availability is a limiting factor.
The net responses of ecosystems to increases in CO2, both directly
and indirectly through changes in temperature and water availability, are
quite complex and only poorly understood. The actual growth enhancements
expected in response to gradually increasing CO2 concentrations are likely
to have only a small and gradual impact on terrestrial ecosystems globally.
Soil Processes and Properties
Temperature changes will have only minimal effects on reaction
rates for inorganic processes in soils, but changes in soil moisture could
have significant effects on rates of diffusion and supply of nutrients to
plants.
Carbon Dynamics
The global pool of carbon is in reservoirs as follows:
Soil | 1500 Gt |
Aboveground biomass | 600-700 Gt |
Atmosphere | 800 Gt |
Ocean | 40,000 Gt |
Both NPP and organic-matter decomposition likely will increase
under increasing temperature. If moisture is readily available,
decomposition of organic matter is likely to be enhanced more than NPP
under global warming, thereby adding more CO2 to the atmosphere. However,
if moisture becomes more limiting then decomposition will be reduced.
Models that take both temperature and moisture into account suggest that
increased NPP would lead to increases in soil carbon under increasing
atmospheric CO2.
Land use is a much more important factor than changes in NPP for
determining soil carbon. Typically about half of the native carbon is lost
from soils when they are put under cultivation over a period of 50-100
years. Minimum tillage practices reduce carbon loss from soils.
Soil Biodiversity
Climate change, specifically changes in temperature and water
availability, could change soil microbial and faunal populations, but
changes in land-use practices are likely to have much greater impact.
However, another element of global change, namely increased deposition of
nitrogen from industrial NOX emissions, is being more widely associated
with major losses of fungi in the root zone in some (particularly forest)
biomes.
Ecological Processes
Organisms interact with their physical environment and with other
organisms to form a complex set of dependencies and interrelationships
sometimes called the "web of life". This interconnectedness makes the
study of impacts of changes in external factors on ecosystems very
difficult. The combinations of all environmental factors and interactions
with other organisms determine the preferred position in an ecosystem for each organism to
live, i.e., its "niche". Some niches are more vulnerable to climate change
than others.
Interactions within ecosystems include competition, herbivory, and
actions of parasites, disease, and mutualists (ecosystem components that
provide mutual benefit, such as pollinating bees and flowering plants).
Communities and Community Dynamics
The collection of different species that interact in a variety of
ways in a defined patch of land is called a community. Communities are
always changing and are subject to "succession", which may be a complete
changeover to another collection of organisms or a more incremental series of
species losses and gains. Loss of one species may provide opportunities
for changes in populations of existing species or gain of new species.
Communities may migrate and disperse as their environmental conditions
change. The rate of change compared to the ability of the community to
move determines whether the community will survive under such changing
conditions.
Ecosystems and Biomes
The community and its abiotic environment constitute an ecosystem.
The biotic and abiotic components may have significant interactions. A
biome is a life zone or biogeoclimatic region that shares a common climate,
soil and collection of plant communities and hence ecosystems. Typical
biomes include desert, scrubland, tundra, bog, forest, rainforest,
woodland, and grassland. A biome consists of plants, animals and the environment that links them.
Ecosystem Breakdown
Models are used to study the interactions within and between
ecosystems. Such studies ultimately are useful to determine the
vulnerability of ecosystems to break-down due to loss of some species or
invasion by others. This may impact the functioning of the ecosystem in
terms of its ability to efficiently use water, light, and nutrients in the
production of plant carbon.
The accompanying figure shows the
changes in natural vegetation for the US as simulated by two different
vegetation models under a doubling of atmospheric CO2. Maps on the
right consider both the climatic and physiological effects of the enhanced
CO2, whereas the maps in the center consider only the climatic effects.
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The next figure gives the change in terrestrial
carbon storage simulated for the US under a doubling of atmospheric
CO2 for various combinations of climate models, biogeochemistry
models, and vegetation models.
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