<?xml version="1.0" encoding="UTF-8"?>
<feed xmlns:dc="http://purl.org/dc/elements/1.1/" xmlns="http://www.w3.org/2005/Atom">
<title>Conference Papers</title>
<link href="http://hdl.handle.net/10453/106" rel="alternate"/>
<subtitle/>
<id>http://hdl.handle.net/10453/106</id>
<updated>2013-05-21T23:20:27Z</updated>
<dc:date>2013-05-21T23:20:27Z</dc:date>
<entry>
<title>Dynamic River-Aquifer interaction modelling and optimal interception of saline groundwater discharge</title>
<link href="http://hdl.handle.net/10453/6712" rel="alternate"/>
<author>
<name>Middlemis Hugh</name>
</author>
<author>
<name>Merrick Noel</name>
</author>
<author>
<name>Williams Robert</name>
</author>
<id>http://hdl.handle.net/10453/6712</id>
<updated>2010-07-21T22:42:30Z</updated>
<published>2005-01-01T00:00:00Z</published>
<summary type="text">Dynamic River-Aquifer interaction modelling and optimal interception of saline groundwater discharge
Middlemis Hugh; Merrick Noel; Williams Robert
Acworth, RI; Macky, G; Merrick, NP
The Murray River reach at Mildura, Australia, has been identified since the early 1970s as a place where&#13;
saline groundwater discharge to the river has been exacerbated by the presence of a weir and a lock. It is believed that&#13;
salt-laden groundwater has been entering the river in response to a normal operating head difference of 3.6 metres&#13;
between upstream and downstream water levels. Deep groundwater, which has salinities several times those of&#13;
seawater moves upwards to the river under a strong vertical gradient.&#13;
In an effort to intercept this flow, the New South Wales Government install ed a dewatering network in 1979&#13;
known as the Buronga Salt Interception Scheme. Effluent is piped to a large gypsum swamp a few kilometres to the&#13;
north. The area has been the subject of several modelling studies since the mid 1980s, initially with an analytical model,&#13;
then a finite element model and more recently a finite difference now model and solute transport model. A coupled&#13;
optimisation model has been used to derive optimal pumping rates for an expanded network of interceprion bores by&#13;
insisting that groundwater heads remain at or below river levels.&#13;
The river and the aquifer system are highly interactive. As a result, there is a highly dynamic variation in&#13;
fluxes 10 and from the riv cr. The latest numerical model replicates the dynamics of the system faithfully. At times of&#13;
high river flow, relatively fresh river water recharges the aquifers. During low river flow, saline groundwater enters the&#13;
river below the weir.&#13;
The river salt load estimates from the solute transport modelling are in good agreement with estimates based&#13;
on multiplying water fluxes with local salinities. Given the good agreement, the latter approach is regarded as a&#13;
sufficient indicator of sail loads. achieved with much less effort. The solute model predicts a "warm spot" immediately&#13;
downstream of the weir, where elevated groundwater salinities can be expected. The solute modelling was useful in&#13;
showing the importance of including the dynamics of hydraulic stresses, rather than the common assumption of steadystate&#13;
flow. It was also instructive in showing the dilution that occurs upstream of tile weir and that flood recharge had to&#13;
be added to the flow model to account for some observed fresh water zones.&#13;
Salt load estimates with transient modelling are about five limes higher than steady-stare estimates. due to river&#13;
dynamics and the slower response time of groundwater. After a high river flow event, groundwater levels near the river&#13;
will remain elevated for some tirrc and salt-laden groundwater will discharge to the river until a new equilibrium is&#13;
achieved. It is ironic that a fresh high flow event in the river causes a subsequent salt pulse in the river due to discharge&#13;
of salty groundwater from a temporary mound.&#13;
It is clear from the simulation modelling, and measured vertical head differences that the interception&#13;
scheme's operation could be improved. The optimisation analysis recommends an increase of about 45% in pumping&#13;
rates.
</summary>
<dc:date>2005-01-01T00:00:00Z</dc:date>
</entry>
<entry>
<title>Towed geo-electrode arrays for analysis of surface water groundwater interaction</title>
<link href="http://hdl.handle.net/10453/6713" rel="alternate"/>
<author>
<name>Allen David</name>
</author>
<author>
<name>Merrick Noel</name>
</author>
<id>http://hdl.handle.net/10453/6713</id>
<updated>2010-07-21T22:39:13Z</updated>
<published>2005-01-01T00:00:00Z</published>
<summary type="text">Towed geo-electrode arrays for analysis of surface water groundwater interaction
Allen David; Merrick Noel
Simms, J
High productivity analysis of surface water groundwater interaction is possible using GPS&#13;
positioned vertical electrical conductivity imaging along with depth recording. Short submerged geoelectric&#13;
arrays provide a great deal of detail right at the base of surface water bodies: however they&#13;
cannot be used in treacherous waterways with debris scattered through them. Long floating arrays can&#13;
be towed through such waterways and have the additional benefit of greater depth of exploration.&#13;
Floating arrays also can have reasonable resolution at the base of surface water bodies provided that they&#13;
are designed optimally and that data from them is inverted effectively. Array design must optimize a&#13;
balance of signal strength maximization, exploration depth resolution weight and drag minimization&#13;
crosstalk and current leakage minimization and simple minimal response to three dimensional&#13;
heterogeneity. Pragmatic interpretation of the huge volumes of data that are typically acquired is best&#13;
achieved using three dimensional "ribbon' images. Prominent features of interest are in most cases&#13;
related to groundwater salinity. Low conductivity anomalies often indicate fresh surface water seepage&#13;
into more saline groundwater. High conductivity anomalies that intersect the bases of surface water&#13;
bodies usually indicate saline inflow to the surface water bodies.
</summary>
<dc:date>2005-01-01T00:00:00Z</dc:date>
</entry>
<entry>
<title>Future roles for native woody species in Australian agricultural landscapes</title>
<link href="http://hdl.handle.net/10453/6714" rel="alternate"/>
<author>
<name>Newton Philip J</name>
</author>
<author>
<name>Yunusa Isa</name>
</author>
<id>http://hdl.handle.net/10453/6714</id>
<updated>2013-04-18T23:44:52Z</updated>
<published>2003-01-01T00:00:00Z</published>
<summary type="text">Future roles for native woody species in Australian agricultural landscapes
Newton Philip J; Yunusa Isa
Wilson, BP; Curtis A
Australian broadacre agricultural lands are dominated by annual crop and pasture species with&#13;
relatively shallow root depths compared to perennial species and low accumulation of above&#13;
ground biomass. Deterioration of the environment in these landscapes by dryland salinity,&#13;
nutrient losses, soil degradation, emission of greenhouse gases and loss of biodiversity may&#13;
be averted by phases of native woody species and shrubs. Recently, lucerne and other&#13;
herbaceous perennials have begun to be incorporated into broadacre cropping systems for&#13;
hydrological control. There are indications, however, that lucerne may not be as efficient as&#13;
woody species in dewatering the soil profile. Some recent studies in America have shown&#13;
that mitigation of net global warming potential by lucerne was significantly less than woody&#13;
species, due to nitrous oxide emissions and lime requirements in the lucerne and resistance of&#13;
woody species to decomposition in the soil. Pastures such as lucerne have different&#13;
biodiversity values compared with native woody species. Phases of different ages of native&#13;
woody species are likely to provide multiple niches for enhanced biodiversity, provided&#13;
biological assets are maintained when cropping and/or pasture phases are resumed. Problems&#13;
perceived with use of woody species often centre on loss of income during the early years of&#13;
their growth. However, forecast markets for emerging bio-energy industries, and ecosystem&#13;
services incentives could provide worthwhile returns. This hypothetical approach using&#13;
native woody species is untested scientifically and research is needed to ascertain their utility&#13;
in a range of Australian environments. The selected examples we have shown focus on&#13;
environmental outcomes and would depend on favourable socio-economic structures for&#13;
implementation. We envisage that optimisation of overall environmental gains could be&#13;
achieved in a six year time frame.
</summary>
<dc:date>2003-01-01T00:00:00Z</dc:date>
</entry>
<entry>
<title>Stream baseflow preservation with optimal aquifer management</title>
<link href="http://hdl.handle.net/10453/6715" rel="alternate"/>
<author>
<name>Alkhatib Mohammed Abdelmohdi</name>
</author>
<author>
<name>Merrick Noel</name>
</author>
<id>http://hdl.handle.net/10453/6715</id>
<updated>2012-11-25T23:49:34Z</updated>
<published>2005-01-01T00:00:00Z</published>
<summary type="text">Stream baseflow preservation with optimal aquifer management
Alkhatib Mohammed Abdelmohdi; Merrick Noel
Acworth, RI; Macky, G; Merrick, NP
The public water supply in the Gosford-Wyong area of New South Wales, Australia, is reliant on streams&#13;
that originate in elevated sandstone country. About half of the stream flow is believed to be baseflow from the&#13;
sandstone aquifer system in the Kulnura-Mangrove area. At the same time as the population is growing steadily on the&#13;
coast, there is increased demand for groundwater for horticultural. agricultural and industrial purposes along the&#13;
sandstone ridges. Hence, good groundwater management is critical, to ensure that stream baseflow is not jeopardised.&#13;
The study area consists of nine catchments and is located north of Sydney and inland from Gosford with an&#13;
area of about 1,400 km2. Baseflow has been estimated for seven flow gauges located at the creeks by applying a digital&#13;
filtering algorithm to separate the baseflow from the total stream flow. The groundwater hydrographs for 20 monitoring&#13;
bores show strong correlation with residual rainfall mass, which suggests that rainfall recharge provides the major&#13;
control on aquifer behaviour. Hydrographs at the same location show that, under natural conditions, there is a huge&#13;
vertical head difference between layers of alternating sandstone (as much as 30 metres).&#13;
A management model that couples a simulation model (MODFLOW -SLRFACT) with an optimisation model&#13;
(OPTl MAQ) has been developed to preserve stream baseflow, MODFLOI,V -SURFACT was selected 10 simulate the&#13;
complex multi-layer Kulnura-Mangrove aquifer system. The model has an area of 40 km x 59 km with approximately&#13;
400 m difference in elevation. The model was divided into 30 flat layers that reflect the alternation between sheet and&#13;
massive facies in the Hawkesbury Sandstone Formation. A uniform cell size 500 m x 500 m results in a grid mesh of&#13;
118 rows and 80 columns. The model was calibrated for both steady state and transient conditions.&#13;
The results of steady-state calibration revealed that the model perfonms very well in representing the values&#13;
and the patterns of the composite groundwater level contours map. Also. the results showed a good agreement between&#13;
the observed and computed target values across all the model layers with a coefficient of determination of 0.994. The&#13;
transient model started in January 1985 and ended in October 2003 with a monthly stress period, The results of the&#13;
transient calibration illustrated that the model matched very well with all observed hydrographs, even in the areas that&#13;
have high vertical head difference, Also, the results showed a good agreement between the estimated baseflow and that&#13;
simulated by MODFLOW -SURFACT for all the flow gauges.&#13;
OPTIMAQ software, based on generic optimisation software (GAMS). solves the management problem with&#13;
linear or nonlinear objectives by using the response matrix approach. OPTIMAQ was linked successfully with&#13;
MODFLOW -SURFACT to compose the management model for the multi-layer aquifer system in the Kulnura-&#13;
Mangrove area. The main target for the management model is to preserve baseflow in the creeks by determining the&#13;
optimal limits on groundwater extraction from the existing or planned bores. The objective function of the management&#13;
model is to maximise the pumping rates of the bores, subject to groundwater level constraints imposed along the creeks.&#13;
In effect, this approach determines a sustainable yield for the aqui fer system that is compliant with surface water&#13;
constraints.
</summary>
<dc:date>2005-01-01T00:00:00Z</dc:date>
</entry>
</feed>
