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Optimisation as tool to explore climate change adaptation possibilities Dr. Jeffery Connor, Stream Leader Water Policy Options Assessment
SA Premier’s Science Fund Project:  Climate Change, Communities and Environment  ,[object Object],[object Object],[object Object],[object Object],[object Object]
Climate challenges Climate impacts on regional water supply and adaptation challenges
Re-live from 1938 2014
Long Run Climate Change Adaptation Evaluatoin -63 -38 -13 Runoff Change (%) -25 -15 -5 Rainfall Change (%) 4 2 1 Temperature Change (°C) Severe Moderate Mild
Climate impacts on regional water supply and adaptation challenges Inflows have dropped 68%  but use has only dropped 12 Back  to  empty
Growing “unlicensed” water taking  0GL 1,200GL 2,400GL 3,600GL
Reforestation
Challenges of South Australia  ,[object Object],[object Object],[object Object]
Three adaptation challenges –  four optimisation/simulation models to help ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Irrigation sector adaptation model 1
Irrigation sector adaptation model 1 ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Reduced water allocation - Short-run analysis of adaptation and economic impact ,[object Object],[object Object]
Longer run challenge – a patchwork of abandoned and still irrigated farms, underutilised infrastructure  ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Adaptation as an opportunity for regional landscape & economy renewal ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Environmental assets and threats ,[object Object]
Regional development assets in Torrumbarry ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Understanding the potential of a transformed landscape: An optimal reconfiguration ,[object Object]
An optimal reconfiguration
Science / engagement challenges ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Portfolio analysis for water supply augmentation ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Portfolio analysis of water supply options ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Optimisation to support environmental water management ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
The approach ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],Integration: Test investment, management options & technical assumptions
Model Structure
Challenges ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Assets public and private benefits Private benefit to irrigators and supply firms from less cost to supply, when land use change allows system rationalisation Water conveyance infrastructure Public benefit from enhanced environmental condition, recreation opportunities if land is retired from irrigation converted to reserves Private benefit if residential development is allowed on contiguous land Private demand for carbon credits if land is revegetated High environmental and amenity value land along water courses, wetlands Public salinity benefit to down stream irrigators, municipal industrial water users as land becomes less utilised for irrigation Private demand for land for dryland farming Currently irrigated areas creating large River Murray salt loads Private benefit to irrigator as better land becomes more fully utilised for irrigation  Soils Highly suited to irrigation Public or private benefits from  change it asset use Asset
Calculating Benefits ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
An optimal reconfiguration 0 11.1 120 $-5.5 $0 $1.7 $0 $4.7 $-11.9 Non-targeted Tender $6.5 $5.2 $4.1 $2.8 $3.9 Value of Dryland Ag $2.5 $2.5 $2.5 $2.5 $0 Sale of Carbon Credits 8.8 8.8 8.8 8.8 0 Carbon Sequestered (million tones CO2 -e ) 10.4 9.5 10.4 9.5 24.5 ECs Avoided 120 60 120 60 120 Water for Environment (GL) $71.0 $79.4 $1.5 $17.8 $-3.6 Total Benefits $3.8 $3.8 $3.8 $3.8 $0 Water Delivery Cost Savings $1.6 $1.4 $1.6 $1.4 $3.7 Downstream Salinity Cost Avoided $56.6 $66.5 $-10.5 $7.3 $-11.2 Value of Irrigated Ag. 100% for the Environment (40% less water) 50/50 New Irrigation/ Environment 100% for the Environment 50/50 New Irrigation/ Environment Targeted Tender (Upper Bound) Targeted Tender (Lower Bound) Salinity-targeted
Water Allocation implications ,[object Object]
Floodplain – lack of inundation is greatest risk to floodplain health
The Murray  Darling Basin 1/7 of area of Australia ½ of value of crop production 80% of irrigation Highly allocated –  27% of natural flow Diversions capped in 1994 Water trade allowed since 1987 Increasing liberalised and Active temporary &  Permanent markets
Talk overview ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Expansionary Phase of MDB water economy 1900 – 1980 (Randall, 1981; Watson and Rose, 1980) ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Maturing Phase of MDB water economy 1980 – ongoing  ,[object Object],[object Object],[object Object],[object Object],[object Object]
Maturing Phase of MDB water economy 1980 – ongoing ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
The ongoing and unfinished agenda of policy for a maturing water economy ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
The genesis of today’s crisis: growing diversions, and extreme variability  Extreme variability (repeated drought)  Growing diversion, even with cap
Floodplain health impacts of climate change Area at risk from  lack of inundation 1964 Area at risk from  lack of inundation 2007
Floodplain health – current drainage management policy is reducing floodplain watertable risk, climate change will reduce this risk further 2050 Lindsay Point Floodplain high watertable floodplain risk Historic drainage rates  Current drainage rates  Moderate Climate change
Lower Murray Futures ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Transdisciplinary and Collaborative Structure:  River Corridor
Water Allocation implications ,[object Object]
Adaptation model ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Reduced water allocation - Short-run analysis of adaptation and economic impact ,[object Object],[object Object]
Long-run analysis of less water ,[object Object],[object Object]
Long-run analysis of less water  ,[object Object],[object Object]
Adaptation ,[object Object],[object Object],[object Object]
Implication at the regional level – a need to adapt ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Path dependence, lock-in, irrigation, regional landscape & economy ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
The adaptation challenge ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Adaptation as an opportunity for regional landscape & economy renewal ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Identifying regional adaptation strategies  with an asset based approach ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Applying an asset based approach to regional adaptation strategy development ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Applying an asset based approach to regional adaptation strategy development  ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Environmental assets and threats ,[object Object]
Regional development assets in Torrumbarry ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Understanding the potential of a transformed landscape: An optimal reconfiguration ,[object Object]
An optimal reconfiguration
Calculating Benefits ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
An optimal reconfiguration 0 11.1 120 $-5.5 $0 $1.7 $0 $4.7 $-11.9 Non-targeted Tender $6.5 $5.2 $4.1 $2.8 $3.9 Value of Dryland Ag $2.5 $2.5 $2.5 $2.5 $0 Sale of Carbon Credits 8.8 8.8 8.8 8.8 0 Carbon Sequestered (million tones CO2 -e ) 10.4 9.5 10.4 9.5 24.5 ECs Avoided 120 60 120 60 120 Water for Environment (GL) $71.0 $79.4 $1.5 $17.8 $-3.6 Total Benefits $3.8 $3.8 $3.8 $3.8 $0 Water Delivery Cost Savings $1.6 $1.4 $1.6 $1.4 $3.7 Downstream Salinity Cost Avoided $56.6 $66.5 $-10.5 $7.3 $-11.2 Value of Irrigated Ag. 100% for the Environment (40% less water) 50/50 New Irrigation/ Environment 100% for the Environment 50/50 New Irrigation/ Environment Targeted Tender (Upper Bound) Targeted Tender (Lower Bound) Salinity-targeted
Realising the potential: what role for market, what role for policy? ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Assets public and private benefits Private benefit to irrigators and supply firms from less cost to supply, when land use change allows system rationalisation Water conveyance infrastructure Public benefit from enhanced environmental condition, recreation opportunities if land is retired from irrigation converted to reserves Private benefit if residential development is allowed on contiguous land Private demand for carbon credits if land is revegetated High environmental and amenity value land along water courses, wetlands Public salinity benefit to down stream irrigators, municipal industrial water users as land becomes less utilised for irrigation Private demand for land for dryland farming Currently irrigated areas creating large River Murray salt loads Private benefit to irrigator as better land becomes more fully utilised for irrigation  Soils Highly suited to irrigation Public or private benefits from  change it asset use Asset
Water trade in diversion not evapotranspiration 100 ML Unconfined Aquifer 50 ML Water that returns  to the aquifer 45 ML Actual amount used 5 ML Evapo- transpiration Drainage
Implications of diversion property rights
The inefficiency of irrigation efficiency investment as environmental flow sourcing policy
 
Salinity externality
The Lower Murray Salinity Issue Lag time ~ 100 years Growing, time delayed, saline groundwater flow into river
Salinity loading and concentration effects of climate change
Fixing the salinity problem engineering - “salt interception”  What is salt interception?
Future Salt Interception cost estimated with optimisation ,[object Object],[object Object],Chowilla (19 895) Rufus River  Murtho Stage 2 (882) Murtho Stage 1 (630) Bookpurnong (3960) Pike Stage 2 (2884) Pike Stage 1  (7249) Loxton (7972) Pyap (470) Kingston East (658) Kingston West (658) Woolpunda Extension (630) Woolpunda  (5 253) Wakerie  (4 344) Wakerie 2L (3 630) Woolpunda South  (Proposed) Stockyard Plain Noora  Qualco sunlands Interception (2 400) Berri and Renmark Irrigation Area drainage (1 000) Rufus River Interception (827) Present capacity: 14 700 Option 1: 13 000 (scale back for env. reasons) Option 2: 16 400 Option 3: 20 200 Present capacity: n/a Option 1: 10 000 Option 2: 14 600 Option3: 12 900 Present capacity: 1 000* Option 1: 5 046 Option 2: 10 700 Option 3: 13 000 Option 4: 25230 *Disposal of 9 000 possible but potential for adverse env. impacts  Present capacity: 4 500 Option 1: 19 940 Option 2: 20 970 ,[object Object],[object Object],[object Object],[object Object],[object Object]
Salt interception Economics Solution for lower bound 2050 salinity growth prediction (67EC) =$129 x 10 6   ($175 x 10 6 )   Solution for upper bound 2050 salinity growth prediction (157EC) =$381 x 10 6   ($527 x 10 6 )
Salt interception economics Conclusions – steeply increasing cost of marginal salinity offset  Lower bound  2050 salinity estimate Upper bound  2050 salinity estimate Conclusions – cost could exceed benefits of additional investment  for plausible salinity growth
“ The country that takes top prize in water management is Australia” The next prize depends upon industry &  community willingness to support pursuit of robust permanent  solutions
Looking Forward - The Big Challenges  ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Thank you Better Basin Futures, Water Policy Options Analysis Stream Dr Jeffery Connor Environmental Economist and Stream Leader Phone:  +61 8 8303 8784 Email:  jeff.connor@csiro.au Web:   www.csiro.com.au/science/WaterPolicyOptions.html Contact Us Phone:  1300 363 400  or  +61 3 9545 2176 Email:  Enquiries@csiro.au  Web:  www.csiro.au

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Dr Jeff Connor at the Landscape Science Cluster Seminar, May 2009

  • 1. Optimisation as tool to explore climate change adaptation possibilities Dr. Jeffery Connor, Stream Leader Water Policy Options Assessment
  • 2.
  • 3. Climate challenges Climate impacts on regional water supply and adaptation challenges
  • 5. Long Run Climate Change Adaptation Evaluatoin -63 -38 -13 Runoff Change (%) -25 -15 -5 Rainfall Change (%) 4 2 1 Temperature Change (°C) Severe Moderate Mild
  • 6. Climate impacts on regional water supply and adaptation challenges Inflows have dropped 68% but use has only dropped 12 Back to empty
  • 7. Growing “unlicensed” water taking 0GL 1,200GL 2,400GL 3,600GL
  • 9.
  • 10.
  • 12.
  • 13.
  • 14.
  • 15.
  • 16.
  • 17.
  • 18.
  • 20.
  • 21.
  • 22.
  • 23.
  • 24.
  • 26.
  • 27. Assets public and private benefits Private benefit to irrigators and supply firms from less cost to supply, when land use change allows system rationalisation Water conveyance infrastructure Public benefit from enhanced environmental condition, recreation opportunities if land is retired from irrigation converted to reserves Private benefit if residential development is allowed on contiguous land Private demand for carbon credits if land is revegetated High environmental and amenity value land along water courses, wetlands Public salinity benefit to down stream irrigators, municipal industrial water users as land becomes less utilised for irrigation Private demand for land for dryland farming Currently irrigated areas creating large River Murray salt loads Private benefit to irrigator as better land becomes more fully utilised for irrigation Soils Highly suited to irrigation Public or private benefits from change it asset use Asset
  • 28.
  • 29. An optimal reconfiguration 0 11.1 120 $-5.5 $0 $1.7 $0 $4.7 $-11.9 Non-targeted Tender $6.5 $5.2 $4.1 $2.8 $3.9 Value of Dryland Ag $2.5 $2.5 $2.5 $2.5 $0 Sale of Carbon Credits 8.8 8.8 8.8 8.8 0 Carbon Sequestered (million tones CO2 -e ) 10.4 9.5 10.4 9.5 24.5 ECs Avoided 120 60 120 60 120 Water for Environment (GL) $71.0 $79.4 $1.5 $17.8 $-3.6 Total Benefits $3.8 $3.8 $3.8 $3.8 $0 Water Delivery Cost Savings $1.6 $1.4 $1.6 $1.4 $3.7 Downstream Salinity Cost Avoided $56.6 $66.5 $-10.5 $7.3 $-11.2 Value of Irrigated Ag. 100% for the Environment (40% less water) 50/50 New Irrigation/ Environment 100% for the Environment 50/50 New Irrigation/ Environment Targeted Tender (Upper Bound) Targeted Tender (Lower Bound) Salinity-targeted
  • 30.
  • 31. Floodplain – lack of inundation is greatest risk to floodplain health
  • 32. The Murray Darling Basin 1/7 of area of Australia ½ of value of crop production 80% of irrigation Highly allocated – 27% of natural flow Diversions capped in 1994 Water trade allowed since 1987 Increasing liberalised and Active temporary & Permanent markets
  • 33.
  • 34.
  • 35.
  • 36.
  • 37.
  • 38. The genesis of today’s crisis: growing diversions, and extreme variability Extreme variability (repeated drought) Growing diversion, even with cap
  • 39. Floodplain health impacts of climate change Area at risk from lack of inundation 1964 Area at risk from lack of inundation 2007
  • 40. Floodplain health – current drainage management policy is reducing floodplain watertable risk, climate change will reduce this risk further 2050 Lindsay Point Floodplain high watertable floodplain risk Historic drainage rates Current drainage rates Moderate Climate change
  • 41.
  • 42. Transdisciplinary and Collaborative Structure: River Corridor
  • 43.
  • 44.
  • 45.
  • 46.
  • 47.
  • 48.
  • 49.
  • 50.
  • 51.
  • 52.
  • 53.
  • 54.
  • 55.
  • 56.
  • 57.
  • 58.
  • 60.
  • 61. An optimal reconfiguration 0 11.1 120 $-5.5 $0 $1.7 $0 $4.7 $-11.9 Non-targeted Tender $6.5 $5.2 $4.1 $2.8 $3.9 Value of Dryland Ag $2.5 $2.5 $2.5 $2.5 $0 Sale of Carbon Credits 8.8 8.8 8.8 8.8 0 Carbon Sequestered (million tones CO2 -e ) 10.4 9.5 10.4 9.5 24.5 ECs Avoided 120 60 120 60 120 Water for Environment (GL) $71.0 $79.4 $1.5 $17.8 $-3.6 Total Benefits $3.8 $3.8 $3.8 $3.8 $0 Water Delivery Cost Savings $1.6 $1.4 $1.6 $1.4 $3.7 Downstream Salinity Cost Avoided $56.6 $66.5 $-10.5 $7.3 $-11.2 Value of Irrigated Ag. 100% for the Environment (40% less water) 50/50 New Irrigation/ Environment 100% for the Environment 50/50 New Irrigation/ Environment Targeted Tender (Upper Bound) Targeted Tender (Lower Bound) Salinity-targeted
  • 62.
  • 63. Assets public and private benefits Private benefit to irrigators and supply firms from less cost to supply, when land use change allows system rationalisation Water conveyance infrastructure Public benefit from enhanced environmental condition, recreation opportunities if land is retired from irrigation converted to reserves Private benefit if residential development is allowed on contiguous land Private demand for carbon credits if land is revegetated High environmental and amenity value land along water courses, wetlands Public salinity benefit to down stream irrigators, municipal industrial water users as land becomes less utilised for irrigation Private demand for land for dryland farming Currently irrigated areas creating large River Murray salt loads Private benefit to irrigator as better land becomes more fully utilised for irrigation Soils Highly suited to irrigation Public or private benefits from change it asset use Asset
  • 64. Water trade in diversion not evapotranspiration 100 ML Unconfined Aquifer 50 ML Water that returns to the aquifer 45 ML Actual amount used 5 ML Evapo- transpiration Drainage
  • 65. Implications of diversion property rights
  • 66. The inefficiency of irrigation efficiency investment as environmental flow sourcing policy
  • 67.  
  • 69. The Lower Murray Salinity Issue Lag time ~ 100 years Growing, time delayed, saline groundwater flow into river
  • 70. Salinity loading and concentration effects of climate change
  • 71. Fixing the salinity problem engineering - “salt interception” What is salt interception?
  • 72.
  • 73. Salt interception Economics Solution for lower bound 2050 salinity growth prediction (67EC) =$129 x 10 6 ($175 x 10 6 ) Solution for upper bound 2050 salinity growth prediction (157EC) =$381 x 10 6 ($527 x 10 6 )
  • 74. Salt interception economics Conclusions – steeply increasing cost of marginal salinity offset Lower bound 2050 salinity estimate Upper bound 2050 salinity estimate Conclusions – cost could exceed benefits of additional investment for plausible salinity growth
  • 75. “ The country that takes top prize in water management is Australia” The next prize depends upon industry & community willingness to support pursuit of robust permanent solutions
  • 76.
  • 77. Thank you Better Basin Futures, Water Policy Options Analysis Stream Dr Jeffery Connor Environmental Economist and Stream Leader Phone: +61 8 8303 8784 Email: jeff.connor@csiro.au Web: www.csiro.com.au/science/WaterPolicyOptions.html Contact Us Phone: 1300 363 400 or +61 3 9545 2176 Email: Enquiries@csiro.au Web: www.csiro.au