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Outcomes of The Living Murray Icon Sites Application Project
Stuart Little
Project Officer, The Living Murray
Environmental MonitoringeWater CRC Participants Forum 23rd November 2011
Context – The Living Murray
The Living Murray aims to return an average of 500GL (long term cap equivalent) per annum of environmental water to 6 “Icon Sites” in the Murray system. Environmental works and measures are being
constructed to support water delivery.
Scope of Project
The Murray Icon sites Application will produce a tool which:
– models ecological responses to watering scenarios; and
– informs trade-offs and decisions when prioritising environmental water allocation under the MDBA's Living Murray program.
Eco Modeller will convert daily time series data from MSM Bigmod
scenario runs into measures of environmental consequence for each
icon site.
These environmental consequences can then be compared across
sites for different environmental watering strategies.
The Plan• Implement existing ecological response models from the Murray
Flows Assessment Tool (MFAT)
• Link ecological response models to improved hydrological modelling
developed for the Icon Sites
• Refine MFAT ecological response models using findings of monitoring
and research at the Icon Sites since MFAT development
• Develop easily interpreted reports of modelling results to inform the
prioritisation of environmental water allocation under the MDBA's
Living Murray program
Tasks of the Project Phases
Phase 1 – 2008 to 2010
• Linking MDBA hydrological modelling to Eco Modeller
• Modelling system development
• Conceptual models of Icon Site responses to flow and ID key ecological assets
• Developing and implementing Ecological Response Models
• Compilation of research data and resources
• Designing and implementing methods of aggregation and reporting of model results
Phase 2 – 2010/2011
• Refine Eco Modeller as required
• Add to MSM Bigmod, to provide
the input time series required
• Develop relevant models for the
remaining Icon Sites
• Develop new models for pest
species
• Model testing to calibrate and
validate habitat prediction models
• Design and implement an
aggregation and reporting format
Linking MDBA Hydrologic Modelling to Eco Modeller – Phase 1
Developed a data handler that:
– Identifies Bigmod files
– Allows users to select a time series for a particular point
in the Murray system
– Search function to make selection of time series easier
Modelling system development – Phase 1
• Aim to fully implement the MFAT models into Eco Modeller,
then upgrade the elements using additional science and data.
• Base models in MFAT had a level of complexity that was not
able to be duplicated in the original design of Eco Modeller
• New ecological models relevant to the Icon Sites were also
too complex
• Need to develop a structure that would allow various
numerical model forms, that must also conform to providing
output in a similar way
Summary
Limitations
Confidence
Plug –in model
Developing and implementing Ecological Response Models – Phase 1
MFAT contained models for up to 30 assets per icon site
– an asset may have several life history stages; and
– be calculated at several sub sites for each site
– used a range of complex equations that also included scores from variables
that remain static when comparing scenarios
30 assets x 6 Icon Sites x 2-3 habitat requirements/life history stages
equals “lots of models”
To handle the implementation of so many models a “generic species
plug in model” was developed
The TLM Generic model principles
A successful water event can be characterised as:
Magnitude or Threshold– minimum depth, discharge, spatial extent
Duration – how long does it last
Timing – what time of year does it occur
Period between events – how long has it been since the last successful watering
Rate of Change – the speed at which the water rises and falls
Bigmod Output
Event
Duration
Timing
Return Period
Result
Threshold
Ecological Modelling – Phase 1
To demonstrate the application of Eco Modeller, two alternative
flow scenarios were modelled, ‘Natural’ and ‘Current’.
• Simple species based comparison showed that in most cases,
the ‘Current’ scenario had much lower average habitat
suitability scores. The current scenario also had a marked
increase in the number of ‘poor’ years across most models.
• There were also some marked differences between species
and even between the life history stages of the same species,
demonstrating the value of modelling habitat requirements at
the life history stage level.
Outcomes from Phase 1
• The Eco Modeller software changed significantly, the changes
show the benefits of eWater’s Application Project/Focus
Catchment approach to software development.
• The results provided an indication of the potential of the Eco
Modeller software to inform water allocation at the flow-regime
scale (i.e. >10 years).
• Changes to software functionality, the individual ecological
response models and improved aggregation and reporting
were recommended to further refine the product to address
the original scope of the project.
Next Steps – Phase 1 leading to Phase 2
• Compilation of research data and resources for all Icon Sites
• Testing and calibration of the ecological response models
• Review of model outputs for various scenarios and
comparisons to actual watering events
• Creating aggregation, reporting and interpretation tools
• Creation of new and/or modification of existing ecological
response models into the future as greater knowledge
becomes available
Testing and Validation - Phase 2
In order to use the habitat suitability models to inform water resource
management options, the models should ideally be well calibrated to
observed habitat condition output.
Limitations
• biological measures are not the same variable as that being
predicted by the models
• lack of long term biological datasets against which to test
The approach used here was to test the performance of the habitat
suitability models against these small biological datasets.
Testing and Validation - Phase 2
Key Steps
• compile appropriate biological data,
• model areas of inundation for Hattah Lakes (for fish and
vegetation analysis) and for all icon sites for the bird
analysis,
• test habitat suitability models with the available data as
well as relate the biological data to simple measures of
inundation
Findings of Testing and Validation
Waterbird models as they stand have limited use due to:
• lack of long term suitable data
• limited understanding of links between inundation and waterbird
responses
Floodplain vegetation models improved via the adaptive process:
• incorporation of rainfall and a decay factor improved correlation
between field data and model scores
• However, the correlation for vegetation models were typically low.
The limited frequency of field sampling is a limitation for validating the
fish ecological response models, and indeed the waterbird and
vegetation models as well.
Lessons Learnt and Recommendations
• Project outcomes are directly proportional to the ability of the
coordinator to drive the project forward
• Calibration and/or validation of models requires long-term,
appropriate datasets
• The development and maintenance of Eco Modeller model
libraries needs to be treated like an adaptive management
process
• Consider the possibility of incorporating uncertainty into the
ecological response models, e.g. by a Bayesian network
approach
Outcomes of the Application Project
We did:
• Use a real-world application of Eco Modeller to improve the tool and add
greater functionality that was relevant beyond the TLM Icon Sites
application
• Develop a generic model format that can be used to build ecological
response models based on flow requirements
We did not:
• Successfully develop and validate models of ecological response for the
TLM Icon Sites
• Develop an aggregation and reporting tool that could be used to inform the
prioritisation of environmental water allocation under the MDBA's Living
Murray program
Thank You
For further information:
Stuart Little
Murray-Darling Basin Authority
02 6279 0568 or 0466 770188