|
Program
A Student Profiles
- David
Forrester
- Samantha
Grover
- Angela Newey
- Grahame Price
- Anna Richards
- Stan Schymanski
- Christine Sefton
- Russell Turner
- Robert Waterworth
- Eddie Webber
- Vanessa Wong
- Ita Yulnafatmawita
- Melanie Zeppel

Dynamics of mixed species plantations
Supervisors: Jürgen Bauhus, Annette Cowie and Ryde James
Despite the potential benefits of mixed species plantations, their
current establishment in Australia is restricted, possibly due do
to a perceived risk of crop failure. The success of mixed species
plantations in improving productivity depends on species interactions,
species composition, proportions of species and the extent to which
the interactions might be influenced by growth limiting resources.
The aim of this project is to:
- identify the growth habits and physiological characteristics
in tree species that will allow an assessment of the likely competition
between species;
- to determine how the ecological interactions between nitrogen-fixing
and non-nitrogen-fixing species change with resource limitations,
in particular water and phosphorus limitations, which are very
common in the Australian environment.
The research makes use of several field trials and a pot trial.
Preliminary results show that mixed species stands of Eucalyptus
and Acacia are more productive than monocultures of either species.
This is partly due to facilitation via nitrogen fixation by Acacia
and accelerated cycling of nutrients in litterfall in mixed species
stands.
The functions and characteristics
of peat soils in subalpine mossbeds in the Australian Alps

Wellington Plain mossbed, Victorian Alps

Soil Carbon Turnover Rates
As A Function Of Depth In The Soil Profile
Supervisors: Dr Richard Greene, Dr Roger Gifford
Objectives:
- To identify the processes controlling soil carbon decomposition
and their relative contributions, as a function of depth.
- To investigate why carbon is longer lived at depth in the soil
profile and determine whether fresh litter inputs are more stable
when allocated at depth in the profile than to the surface soil
layers.
Background: Soil organic matter is a
critical component of the biosphere with direct links to atmospheric
composition and to agricultural production and sustainability. Much
of the work on soil organic matter to date has focussed on the top
10-20cm of soil, and while this is the zone of greatest carbon/organic
matter concentration, a considerable amount can lie below 20cm. As
most plant roots extend well below 20cm depth and cumulative carbon
stocks in deep soil layers can be significant, an understanding of
the processes controlling carbon turnover and nutrient cycling in
the deeper soil layers is important from both an agricultural production
perspective and that of a carbon sink perspective. In fact there is
some evidence to suggest that the processes controlling organic matter
decomposition at depth may differ from those at the surface, so that
extrapolations from existing information about surface soils to deeper
layers may be of limited value.
Current models used for greenhouse accounting purposes, to estimate
carbon fluxes from below ground sources, are also based on data
from just the top 20cm of soil. While there is some evidence to
suggest that fluxes from deep soil layers may be insignificant relative
to those of the surface layers, despite the presence of significant
carbon stocks at depth, this assumption is in need of verification.
Moreover, if C fluxes from deep soil layers are small as a result
of greater organic matter stability at depth, an opportunity may
exist whereby effective C sinks may be designed to exploit this
situation for maximum sequestration potential.
This project will contribute to the parameterisation of carbon
cycle models through process understanding of C dynamics at depth
in the soil. This will help to improve predictions of carbon fluxes
from below ground sources and inform the process of carbon sink
design.
Experimental Approach:
- Changes in the ratio of naturally abundant carbon isotopes (d13C/12C)
were measured in an experiment designed to trace the rate of decay
of organic matter in the soil as a function of depth, in a field
site where a C4 pasture had been converted to C3 pasture species.
Issues with the use of this technique, relating to changes in
isotopic signatures when C3 and C4 plant materials have been subjected
to burning, have been identified by Evelyn Krull (CRC for GA,
unpublished). The results from this experiment together with Krull's
findings, identify some constraints to the use of stable isotopes
in organic matter studies.
- A large scale litter-bag study is being conducted, involving
burial and subsequent exhumation of 1788 litter-bags containing
a range of different organic materials. The experiment investigates
the effects of litter input quality and soil environmental factors
on organic matter decomposition, and how these effects may vary
with depth.
- A series of soil incubation/respiration experiments are being
run:
- To investigate the relative amounts of labile and slow pool
organic matter that occur at various soil depths, in certain
selected soil profiles,
- To verify that observations from the litter-bag field study
are reproducible in the lab under controlled conditions and
in different soil types, and
- Test hypotheses regarding the underlying processes that
may be causing the observed field phenomena.
 |
Carbon sequestration
implications of forest health
Above- and below-ground carbon
dynamics in tropical mixed species forest plantations

Ecological optimality
and model parameterisation
Juvenile eucalypt leaf morphology
Supervisors: Prof. Jann Conroy, UWS, Dr Kelvin Montagu, SFNSW,
Assoc. Prof. Brian Atwell, Macquarie University.
Leaves share common function yet show remarkable diversity in their
form. The way in which leaf dry matter is organised is crucial for
light capture, gas exchange and thus CO2 assimilation. Specific
leaf area (SLA), the leaf area per unit leaf dry mass, appears to
be the most useful summary parameter to measure the display of leaf
dry matter. SLA (or its component parts leaf thickness and density)
has been suggested to be indicative of ecological strategy. It has
also been shown to correspond to resource use efficiency (water
and nitrogen), leaf scale assimilation and relative growth rate.
Leaf morphology varies not only between species but also within
species as the result of light, nutrition, atmosphere, temperature,
water availability and ontogeny. Leaf morphology is thus undoubtedly
a key factor that contributes to whole plant growth. However, it
is surprising that leaf morphology and anatomy has not been more
intensively investigated among eucalypt species that are economically
and ecologically important. The aims of my research are to establish
the nature of the variation in leaf morphology and anatomy between
eucalypt species and in response to changing environment. Further,
how does leaf morphology contribute to growth rate, and can seedling
leaf traits be used to identify long-term growth potential for use
in forestry applications?
My research has involved experimentation in controlled environment
glasshouses (UWS and Macquarie University) and in the field (UWS
and NSW State Forests). Interspecies variation (11 species) and
intraspecies response to environment (light, CO2 and temperature)
was investigated in seedlings grown in glasshouses. In these experiments,
whole plant growth analysis, juvenile leaf anatomy and leaf gas
exchange was examined. A field trial of 12 species was established
in April 2000 at the Yarramundi paddocks, UWS Richmond for comparison
of field-grown and glasshouse-grown plants. Seed from State Forest
Provenance trials was grown in a glasshouse trial to establish the
relationship between seedling growth and leaf morphology with that
of mature plantation trees, and thus infer the usefulness of seedling
parameters to screen genotypes for plantation growth.
Examining the use of LIDAR
and Synthetic Aperture RADAR for estimating above ground woody biomass
in coastal production forests
Supervisors: Prof Tony Milne, Dr Kelvin Montague
Objectives: This study aims to develop
forest above-ground biomass classification models with both RADAR
and LIDAR sensors using stand structure attributes, and to compare
advantages and limitations of each imaging technique. This research
will also explore the options for combined RADAR/LIDAR biomass modeling
(or data fusion). The intention is to investigate alternative RADAR
and LIDAR remote sensing technologies that have the potential to
provide objective and cost effective above-ground biomass estimates
on a local forest scale.
Introduction: Since the Kyoto Earth
Summit (1997) there has been growing interest in remote sensing
techniques for estimating above-ground biomass in Australian forests
for carbon credit accounting and auditing. State Forests of NSW
manage over 2.9 million ha of public forest representing a significant
carbon store. As harvesting events are the prime process for varying
carbon storage in these forests (both spatially and temporally)
it is important to develop remote sensing techniques for biomass
classification that can deal with the complex floristic and structural
variation of harvested forests.
RADAR (Radio Detection and Ranging)
studies have traditionally focused on microwave backscatter intensity
(or return signal strength) to classify forest biomass. Backscatter
is influenced by band wavelength, sensor viewing geometry, target
properties and terrain characteristics (topography and soil moisture),
and has been shown to saturate at high biomass levels. These constraints
have limited RADAR applications to low biomass open forests on relatively
flat terrain. Unfortunately, most coastal regrowth forests in NSW
have high biomass levels (150 to 350 t/ha) growing in steep terrain.
If imaging RADAR is to provide regional wall-to-wall biomass estimates
then new techniques are required to overcome existing limitations.
Alternative RADAR variables, such as band ratios, polarisation properties
(scattering measures) and spatial texture, are being examined.
LIDAR (Light Detection and Ranging)
offers an objective tool for mapping complex spatial variation in
natural forests and woodlands. High resolution airborne laser scanners
can record millions of x, y and z coordinates of forest structure
from which a 3D tree canopy surface can be generated. This data
can subsequently be used to infer forest parameters such as stand
height, crown area, spacing and stocking.
Experimental approach: A case study
site in Ourimbah State Forest was chosen as a representative example
of coastal regrowth production forest in Hunter Region (NSW). It
contains a diverse range of vegetation communities within a mix
of harvested and unharvested stands spread across moderate to steep
terrain. Following the integrated harvesting of the compartment,
both intensive (2ha) and extensive (30m radius) plots were established.
A range of remote sensing datasets, including SAR, LIDAR, multi-spectral
video and aerial photography, have been acquired to assist in developing
forest biomass classification models. This study will initially
investigate independent SAR and LIDAR derived total above-ground
biomass classification models in a harvested coastal hardwood forest.
As a follow on, it may be possible to improve remote sensing forest
biomass predictions through data fusion of SAR and LIDAR imagery
either at the pixel or feature level.
 |
 |
Prediction of forest growth
in mid to low rainfall forest systems using process-based models

The Dynamics of Carbon Sequestration
in Coarse Woody Debris of Eastern and SW Australian Forests.
Supervisors: Dr Cris Brack
Description: This study is aimed at
defining the decay dynamics of coarse woody debris (CWD) in different
forest types along a latitudinal gradient. The quantity of carbon
(C) stored in different decay classes, and the movement of the CWD
between the different decay classes, is of major importance when
accounting the sequestered C in these forests. Modelling of this
pool of sequestered C will lead to the formulation of management
strategies for CWD in these forest types, which is currently lacking.
Surveying of CWD will be done at Atherton Tableland (tropical rainforest)
and Rockhampton (eucalypt woodland) in Queensland, southern Tasmania
(eucalypt plantations), and in SW Western Australia (eucalypt plantations).
Due to the slow rate of decomposition of CWD, and the short duration
of this project, CWD decomposition will be surveyed using the chronosequence
method. This method involves the surveying of CWD of different ages
at the one time.
CWD will be surveyed in the field with the use of the line-intersect
method. This will give a volume of CWD (per hectare) for each decay
class. CWD samples of different decay classes will be analysed in
the lab for density and chemical constituents. The density of the
lab samples will be used to calculate the mass (per hectare) of
CWD at each location, based on decay class. The line transects are
triangular, with each side being 100 m long (total transect length
of 300 m). This triangular arrangement is necessary in order to
account for any orientation bias, especially in areas with high
gradients.
The effect of salinity
and sodicity on soil carbon stocks and fluxes

The Influence of Organic Matter
on Soil Structural Stability and CO2 Release during Cultivation
Supervisors : H.B.So1), N.W.Menzies1), and R.C.Dalal2) (1).
Univ. of Queensland, 2) CRC-GA, QDNR)
Abstract: This project aims to investigate
the role of OM in improving soil structural stability and also the
function of structured soils in protecting SOM against oxidation.
How strong the OM binds soil particles/aggregates, where it can
be found within aggregates, what type of the OM presents, and how
long it can stay in each aggregate fraction were assessed. Seven
(7) soils with different textures, clay mineralogy, as well as land
use were investigated. Soil aggregates were fractionated into 3
different sizes (>20, 2-20, and <2 um) using 3 rates of energy application
of 0.04, 0.06, and 0.20 Jg-1 soil (Fig. 1). For each soil type,
fifteen soil separates were obtained in this process. It was assumed
that aggregates collected after application of specific rate of
energy, had bonding energy which was greater than or the same as
the energy level applied.
Generally, the result showed that most soils have high %OC in smaller
aggregate sizes, either in the 2-20 or <2 um, and low in aggregates
>20 um, except for the Ferrosols (ORP and ORF). In ORP soil (Fig.
2), the <2 um fractions had the lowest OC contents, lower than the
OC of the bulk soil. The fractions >20 and 2-20 um had higher OC
contents than the bulk soil, and the highest absolute OC value was
found in aggregates >20 um. The reverse occurs with the Black Earth
(BE) soil (Fig. 2), aggregates >20 um had the lowest OC contents,
which decreased with increasing energy levels. Although some aggregates
<2 um had higher OC content than that of 2-20 um, the absolute highest
value of the OC was found at aggregates 2-20 um.
The susceptibility of SOM in each fraction to oxidation was measured
under laboratory conditions through CO2 emission using Licor-6400
(Fig. 3). For both soils, BE & ORP, CO2 emission from aggregates
<2 um was greater than that from the aggregates >20 and 2-20 um,
as well as from unfractionated bulk soil. Low CO2 emission rate
at 2-20 um fraction was also found at both soils. The higher rates
of CO2 emission from those fractionated soils compared to the bulk
soils indicate that SOM was not sufficiently exposed to oxygen until
they were broken into <2 um size fractions, where some of the SOM
would have been found on the outer surfaces of these fractions.
Therefore, it appears that SOM is partly protected within soil aggregates.
The implication of these findings is that excessive cultivation
will increase the rate of SOM degradation significantly.
|
|
| Figure 1: Energy levels used to break bulk soil
aggregates |
Figure 2: OC content (%wt) of ORP and BE soil
fractions |
 |
Figure 3: CO2 release measurement
using Licor-6400 at laboratory |
Tree growth, water use and
dryland salinity
Supervisors:Professor Derek Eamus, DR Brad Murray and DR Craig
Barton
My project aims to:
- compare tree growth, carbon accumulation and water use between
a remnant forest and plantation forest in the same locality,
- establish relationships among tree growth, tree water use, leaf
area, and basal area, and (c) compare tree growth and water use
between saline and non-saline areas.
By comparing growth and water use of native vegetation and planted
forests in a common location, we shall significantly improve our
ability to apply a scientific understanding to the problems of land
management brought about through changes in land use.
This project will determine seasonal tree growth and water use
patterns over a three-year period. The information on species survival
and growth under different salinity conditions will also provide
pertinent information for greenhouse accounting. Knowledge of amounts
and change in carbon stocks resulting from salinisation is fundamental
to emissions accounting and a national carbon inventory.
Relevance and Significance to the CRC of Greenhouse
Accounting: This project is relevant to the CRC's investigations
on dryland salinity and the effects on carbon sequestration. This
project will determine seasonal tree growth and water use patterns
over a three-year period. The information on species survival and
growth under different salinity conditions will also provide pertinent
information for greenhouse accounting. Therefore, this project contributes
to the overall vision of the CRC to provide research outputs for
greenhouse emissions accounting at the national and project level.
Knowledge of amounts and change in carbon stocks resulting from
salinisation is fundamental to emissions accounting and a national
carbon inventory.
|