Greenhouse
Accounting PhD Thesis Topics: 2002-2005
1. Role of
Vegetation Type in Soil Organic Matter Accumulation
CRC Program A: Measurement
& Spatial Estimation of Carbon Pools and their Turnover
Project A1: Belowground
Carbon Dynamics
Contact: Dr
Roger Gifford (roger.gifford@greenhouse.crc.org.au)
A preponderance
of world literature on soil carbon-stock change ofter the conversion
of pastures to forest indicates that pine trees tend to reduce soil
organic matter stocks despite the much greater carbon stocks
aboveground and in surface litter and the lack of vegetation removal
by grazing. It is not known why.
Of
several hypotheses that seek to explain the observation above, one is
that pine roots may foster more rapid soil organic matter decomposition,
relative to pasture. This might come about via material excluded from
pine roots, from the character of the soil microbial populations supported
by pines compared with pastures, or the effect of pine roots compared
with the effect on pasture roots on soil structural stability and hence
organic matter stability. Another hypothesis is that the removal of
N-fixing legumes present in pastures when pines establish, causes loss
of ecosystems C-stocks and consequentially, aloss of soil carbon. It
has been further hypothesised that the reduction in organic matter is
primarily due to the reduction of the active fast-turnover fraction
of the soil orgainic carbon.
The
Cooperative Research Centre (CRC) for Greenhouse Accounting is setting
up a 2 to 3 year field study in the Australian
Capital Territory (ACT) where pine forest and improved pasture sites
are located immediately adjacent to native pasture from which they both
developed. The study will evaluate up to ten hypotheses relating to
the change in soil C stocks following land cover change that includes
the above hypotheses. The context of this work is to assist the development
of methodologies to calculate expected CO2 emission
or uptake by the soil folllowing land use change for the natinal effort
to comply with the intent of the Kyoto
Protocol.
The
CRC invites PhD proposals that develop one or more of the hypotheses
above
as a contribution to the larger study.
2. Changes
in Tree Carbon Allocation in response to Water Availability
CRC
Program A: Measurement
& Spatial Estimation of Carbon Pools and their Turnover
Project A2: Carbon
Stored in Woody Vegetation
Contact: Dr Kelvin Montagu (kelvin.montagu@greenhouse.crc.org.au)
Water
limitation on plant growth is ubiquitous in the Australian landscape.
Studies in this area will quantify the impact of water availability
on root:shoot ratios.
Water
availability to trees can vary for a number of reasons. These include
absolute rainfall, the season in which it falls, the vapour pressure
deficit during water use by the tree, the ability of the soil to store
water (soil depth and texture) and additional water sources (water tables
and lateral flow of water) will all affect the availability and use
of water by the tree.
A simple
aridity index may be calculated as the ratio of rainfall to potential
evaporation. Such a ratio only accounts for some of the variation in
water availability. To account for the all source ratio requires an
integrated assessment of the water availability as seenn by the tree.
Isotope discrimination (carbon and oxygen) measurements provide a long
term averaged measure of the soil - atmosphere water balance. Potentially
such measurements may account for many of the finer scale variations
outlined above.
3. Topography-fuel
Modelling for Carbon Accounting
CRC
Program B: Projecting
Changes in the Carbon Cycle
Project B3: Ecosystems
Vulnerable to Change
Contact:
Dr Brendan Mackey (brendan.mackey@greenhouse.crc.org.au)
Fire models
are currently constrained by the lack of data about spatial variability
in fuel across landscapes. Fine scale topographic controls on soil water
and surface radiation results in landscape heterogeneity in litter production
and decomposition rates, and consequently fire regimes. Thus different
parts of the landscape can experience variable fire regimes, in terms
of fire intensity and the mean fire interval, which is an important
factor in Net Biome Productivity.
4. Hydrological
Flux of Carbon
CRC
Program B: Projecting
Changes in the Carbon Cycle
Project B3: Ecosystems
Vulnerable to Change
Contact: Dr Brendan Mackey (brendan.mackey@greenhouse.crc.org.au);
or
Dr Stephen Roxburgh (stephen.roxburgh@greenhouse.crc.org.au)
There
is very little known about the lateral loss of carbon from catchments
as a result of hydrological flows. The little that is known suggests
that it is possible for landscape ecosystems to continue functioning
as carbon sinks (due to the hydrological flux of carbon), even when
biomass and soil carbon have reached equilibrium.
5. Climatic
Variability and Net Biome Productivity
CRC
Program B:
Projecting Changes in the
Carbon Cycle
Project
B3: Ecosystems
Vulnerable to Change
Contact:
Dr Brendan Mackey
(brendan.mackey@greenhouse.crc.org.au);
or
Dr Janette Lindesay (janette.lindesay@greenhouse.crc.org.au)
Regionally-scaled
global circulation models (such as the CSIRO regional model, DARLAM)
do not currently have the capacity to capture mesoscale climatic regimes
at a resolution commensurate with landscape processes. However, these
models can generate useful scenarios indicating broad climatic trends.
Scenarios can also be derived using downscaling techniques applied to
Global Climate Model output data. The challenge is to develop a quantitative
understanding of past and current climatic variability, in order to
determine the potential significance of the projected climatic trends
for Net Biome Productivity.
6. Modelling
Net Ecosystem Carbon Exchange of Woodland Systems in NE Australia
CRC
Program C:
Systems Development and Support
Project
C2: Process
modelling and testing
Contact:
Dr Miko Kirschbaum
(miko.kirschbaum@greenhouse.crc.org.au)
The
project involves using a physiologically-based modelling approach to
model the growth, death and decomposition of woodland systems under
normally varying climatic conditions. The project would use the TRAPS
data set (developed by CRC Member, Dr Bill Burrows, Qld DPI) as the
primary data set for testing. As part of this project, one aim is to
extrapolate findings from the individual patch scale to the Australian
continent.
7. Decomposition
of Residues from native Australian Vegetation: a Quantification of Chemical
Changes and Soil Inputs
CRC
Program A: Measurement
and Spatial Estimation of Carbon Pools and their Turnover
Project
A1: Belowground
Carbon Dynamics
Contact:
Dr Jan Skjemstad
(jan.skjemstad@greenhouse.crc.org.au);
or
Dr Jeff Baldock (jeff.baldock@greenhouse.crc.org.au)
Soil
organic carbon contents are a function of the balance between inputs
and mineralisation. Inputs are dependent on the productive capability
of the site as defined by vegetation type, climate, and fertility, which
all have the capacity to regulate the amount of biomass entering the
soil system. The
mineralisation of these inputs depends on their chemical composition
and any protection offered by the soil matrix. In the proposed work,
the carbon balance and chemical changes (structural chemistry and isotopic
composition) associated with the decomposition of residues derived from
Australian native vegetation will be studied. The proportion of residue
carbon that finds its way into the soil and the subsequent biological
stability and position of the carbon within the soil matrix will be
quantified. In addition, the isotopic changes associated with the changes
in chemical composition will be examined to further our understanding
of carbon balance calculations based on C3-C4
transitions. It is important to define the mechanisms that enhance or
protect residue-derived carbon from mineralisation, in order to assess
the impacts of land use change on soil carbon stocks.
8. Impacts
of Salinity on Soil Carbon Stocks and Fluxes
CRC
Program A: Measurement
and Spatial Estimation of Carbon Pools and their Turnover
Project A1: Belowground
Carbon Dynamics
Contact: Dr Ram Dalal (ram.dalal@greenhouse.crc.org.au);
or
Dr Surender Mann (surender.mann@greenhouse.crc.org.au)
The behaviour
of carbon in saline soils is not very well understood worldwide. Nearly
11 million hectares of land throughout the world is being converted
to saline land each year. The basic task in this project is to investigate
the underlying processes (chemical, physical and biological) involved
in the breakdown of organic matter to form a part of soil, particularly
in saline environments. Some of the key questions that the student will
investigate are:
The behaviour
of soil organic carbon is affected by climatic conditions; hence the
student would be required to investigate these issues in Queensland
and in Western Australia.
9. Carbon Dioxide
and Nitrous Oxide Emissions from Soil following the Ploughing of Legume
and Legume-grass Leys
Improved
ley pastures are the salient features of sustainable farming in Australia.
The ley pasture systems (pasture legume/crop or pasture legume + grasses/crop
of variable duration) occupy over 21 million hectares of Australia,
varying in climate from "Mediterranean" to "tropical".
Although the tropical regions had not used ley systems
widely,
adoption is steadily increasing on fertility-depleted lands, mainly
due to a highly variable climate and thus uncertain responses to fertilisers,
but also due to increasing fertiliser nitrogen costs.
It
has been estimated that improved ley pastures could store 10.8 million
tonnes CO2-equivalent per year during the ley
phase. Since atmospheric N2 is also usually fixed
as organic N, there is a potential for nitrous oxide emissions following
ploughing of legume and legume-grass leys in the tropics. However, there
is very limited information available on carbon dioxide and nitrous
oxide emissions following the ploughing of legume and legume-grass leys.
We
require field studies in the tropical environment to quantify carbon
dioxide and nitrous oxide emissions from different soil depths at the
termination of the ley phase at different times of the year. These studies
need to be linked to controlled environment studies in the laboratory
to quantify the effects of temperature, moisture, carbon and nitrogen
substrates (various carbon pools), and aeration on carbon dioxide and
nitrous oxide emissions from these soils. This study will provide an
important input to the Australian
Greenhouse Gas Inventory on the emissions of nitrous oxides, which
may counterbalance the benefits of enhanced carbon sinks by ley pastures.
The study will also provide a better understanding of below-ground carbon
dynamics in ley systems in the tropics.
CRC
Program A:
Measurement and Spatial Estimation
of Carbon Pools and their Turnover
Project A1: Belowground
Carbon Dynamics
Contact:
Dr Ram Dalal
(ram.dalal@greenhouse.crc.org.au)
or Prof. Graham Farquhar (graham.farquhar@greenhouse.crc.org.au)
or Mr John Carter (john.carter@greenhouse.crc.org.au)
10. Potential
of Zero Tillage Practices to Sequester Carbon in Soils under Continuous
Cropping
CRC
Program A: Measurement
and Spatial Estimation of Carbon Pools and their Turnover
Project A1: Belowground
Carbon Dynamics
Contact: Dr
Ram Dalal (ram.dalal@greenhouse.crc.org.au)
There
is an age-old perception that tillage enhances the decomposition of
organic matter in soil by changes in temperature and moisture fluxes,
aeration, exposure of new surfaces through aggregate disruption, increasing
plant residue-microbial contact, reduced organic material additions,
and frequently leads to increased soil erosion. Therefore, by reducing
or eliminating tillage we can theoretically sequester more carbon in
soil.
Many
countries, including the USA, thus advocate the inclusion of zero-till
(no-till) practices in Additional Activities, Article 3.4 of the Kyoto
Protocol for the consideration of soil carbon sinks. A number of
studies in the USA have shown that soil under no-till practices retains
about 28% more carbon that that under conventional tillage. On the other
hand, results to date in Australia are conflicting. They show increases,
decreases, nil or at the most very small effects on soil carbon storage
under zero-till systems.
We
are not entirely certain about the processes involved in litter (or
plant residue) decomposition as a function of placement, moisture, temperature,
soil type, and litter quantity and quality under zero-till and conventional
till systems. We require specific studies to quantify the effect of
these variables on carbon retention so that we are in a position to
address the effect of zero-till on carbon storage, since Australian
farmers are increasingly using no-till practices and the zero-till area
will continue to increase. These studies will require the measurement
of various carbon pools, and also direct measurement of carbon dioxide
and nitrous oxide emissions from soil.