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Sam Aminfard CATEE 2017 – Texas Energy Summit November 15, 2017

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Presentation on theme: "Sam Aminfard CATEE 2017 – Texas Energy Summit November 15, 2017"— Presentation transcript:

1 Sam Aminfard CATEE 2017 – Texas Energy Summit November 15, 2017
Technical and Economic Potential of Purifying Brackish Groundwater on Texas State Lands Using Integrated Renewables and Desalination Facilities Sam Aminfard CATEE 2017 – Texas Energy Summit November 15, 2017

2 The energy required to desalinate water was estimated using the well data for salinity and depth
High : 19.5 kWh/kgal Low : 2.0 kWh/kgal Desalination Energy Intensity High : 19.5 kWh/kgal Low : 2.0 kWh/kgal Desalination Energy Intensity The energy intensity of desalinating water rises with salinity.

3 High resolution maps of capacity factor for wind and solar resources were employed

4 Local water prices can determine the economic viability of desalination

5 We identified 193 sites that have estimated water costs lower than local municipal prices.
Water Cost [$/kgal] Wind Solar Down-Selected Sites for Local Economic Viability Min Max Mean # Solar Wind

6 Projected water need can also be used to select sites in water stressed areas.
2020 Annual Water Need by County [billion gal] Water Cost [$/kgal] Wind Solar Min Max Mean # Solar Wind

7 Sam Aminfard F. Todd Davidson, Ph.D. sam.aminfard@utexas.edu
Graduate Research Assistant Webber Energy Group The University of Texas at Austin Research Associate | Lecturer Webber Energy Group | Energy Institute The University of Texas at Austin

8 Backup

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11 Compared to 2014, TX is expected to consume 30% more water annually by 2020*
* Texas Water Development Board, “2017 State Water Plan”, Austin, TX (2016)

12 Compared to 2014, TX is expected to consume 30% more water annually by 2020*
* Texas Water Development Board, “2017 State Water Plan”, Austin, TX (2016)

13 How will we address potential shortages?
Compared to 2014, TX is expected to consume 30% more water annually by 2020* How will we address potential shortages? Conservation of existing fresh water resources Increase supply of fresh water * Texas Water Development Board, “2017 State Water Plan”, Austin, TX (2016)

14 There are major barriers to this strategy:
Desalination of brackish or saline water can vastly increase fresh water supplies There are major barriers to this strategy: High capital costs Significant energy demands

15 TX has significant brackish groundwater resources
TX has significant brackish groundwater resources. With sponsorship from the Texas General Land Office, we studied the technical and economic potential to purify brackish groundwater on state lands using integrated renewable energy.

16 Executive Summary We investigated 1,445 TX GLO sites to determine the cost of desalinating brackish groundwater with wind and solar Estimated costs were lower at 193 sites Wind was cheaper at 145 sites Solar was cheaper at 48 sites Many sites with relatively low desalination costs are in regions with high projected water demand

17 Desalinating brackish groundwater with renewable energy can be cost-competitive.

18 Desalinating brackish groundwater with renewable energy can be cost-competitive. The strategy is most competitive in water stressed regions with shallow, low salinity aquifers and abundant renewables resources.

19 Methods

20 Well data was gathered from the Texas Water Development Board database

21 Well data was gathered from the Texas Water Development Board database
Sea Water ~ 35,000 mg/L TDS

22 Wells shallower than 10 ft with salinity below 1000 mg/L were removed

23 Well depth was interpolated across Texas for wells >10 ft and >1000 mg/L
Well data from TWDB used to create maps

24 TDS was interpolated for wells >10 ft and >1000 mg/L
Well data from TWDB used to create maps

25 Regions without brackish groundwater were removed
Well data from TWDB used to create maps

26 The interpolated data for well depth and salinity levels were overlaid to determine energy requirements for desalination Well Depth + Well Salinity

27 Renewable Resources

28 Class 3 and higher regions are generally considered suitable for utility-scale wind turbine applications

29 Solar energy resources are abundant but vary across the state
For comparison Germany has kWh/m^2/day

30 Texas receives almost double the solar energy per square meter as Germany every year
For comparison Germany has kWh/m^2/day Source: NREL

31 The best wind and solar resources are in Western Texas

32 Infrastructure

33 Presence of water infrastructure indicated by public wells and surface water intakes.

34 The distance to wells and surface water intakes was calculated across Texas
We assume that the maximum pipeline length will be the distance to the nearest well or intake. Additional investigation might find closer connections.

35 Estimating Cost

36 Cost estimates are generated using the TWDB’s Unified Costing Model
TWDB developed a publicly-available tool for estimating the cost of water infrastructure projects to unify and support regional and state water plans. We adapted the formulas and interpolated data tables in this tool to generate cost estimates for desalination plants and their supporting infrastructure (pipelines, pumps, wells, etc) Our model tags the local resource data in the previous slides to each GLO site. These are used as inputs to size a renewables-integrated brackish water reverse osmosis project and estimate the cost of water at each site

37 The cost of desalinated water varies significantly based on the location
1 MGD Water Cost w/ PV [$/kgal] Estimated prices for using Solar Power Mean: 4.25 Municipal Rates: 0.10 – $/kgal

38 A concentrated brine is produced during the desalination process that needs to be disposed of -- disposal can be outsourced or a salt water injection (SWI) well can be drilled or purchased. We assumed that a >0.25 MGD (~6000 bbl/day) SWI well would be drilled onsite at an estimated cost of $3 million. This well could handle the disposal needs of a 1 MGD desalination plant with an assumed recovery rate of 80%.

39 The cost of desalinated water varies significantly based on the location
1 MGD Water Cost w/ PV and Disposal [$/kgal] Estimated prices for using Solar Power Mean: 5.05 Municipal Rates: 0.10 – $/kgal

40 The cost of desalinated water using wind is approximately $0. 16 -- $1
The cost of desalinated water using wind is approximately $ $1.12/kgal less expensive than solar. 1 MGD Water Cost w/ Wind [$/kgal] Estimated prices for using Wind Power Mean: 4.21 Municipal Rates: 0.10 – $/kgal

41 The cost of desalinated water using wind is approximately $0. 16 -- $1
The cost of desalinated water using wind is approximately $ $1.12/kgal less expensive than solar. 1 MGD Water Cost w/ Wind and Disposal [$/kgal] Estimated prices for using Wind Power Mean: 5.01 Municipal Rates: 0.10 – $/kgal

42 Local water prices can determine the economic viability of desalination
Min. Muni. Water Price[$/kgal] Mean: 4.82

43 Local water prices can be used to limit potential projects to areas where production costs are competitive 1 MGD Water Cost w/ PV and Disposal [$/kgal] Estimated prices for using Solar Power Mean: 4.23

44 Using wind power produces similar results as solar for determining which sites are competitive with municipal water 1 MGD Water Cost w/ Wind and Disposal [$/kgal] Estimated prices for using Wind Power Mean: 4.17

45 Summarized Results

46 Combining the previous maps gives the lowest water production cost using wind or solar power
Water Cost [$/kgal] Down-Selected Sites for Local Economic Viability Min Max Mean # Solar Wind

47 Projected water need can also be used to select sites in water stressed areas.
2020 Annual Water Need by County [billion gal] Water Cost [$/kgal] Wind Solar Min Max Mean # Solar Wind

48 Conclusions Desalinating brackish groundwater with renewable energy can be cost-competitive The large number of economically competitive sites shows potential for desalination on Texas GLO land using renewable energy Further research must be done to more precisely determine the cost and viability of projects at specific locations El Paso County presents an interesting mix of results and variables worth further investigation Wichita Falls for cheap wind Hudspeth and Presidio Counties for cheap solar Reeves County for GLO availability, aquifer data, O&G markets. Mix of wind and solar.

49 Only considering GLO land with Class 3+ Wind limits the number of potential sites
1 MGD Water Cost w/ Wind and Disposal [$/kgal] Estimated prices for using Wind Power Mean: 4.20 Municipal Rates: 0.10 – $/kgal

50 Local water prices can be used to limit potential projects to areas where production costs are competitive. These results do not include disposal. 1 MGD Water Cost w/ PV [$/kgal] Estimated prices for using Solar Power Mean: 3.52

51 Using wind power produces similar results as solar for determining which sites are competitive with municipal water. These results do not include disposal. 1 MGD Water Cost w/ Wind [$/kgal] Estimated prices for using Wind Power Mean: 3.47

52 Adding disposal costs and limiting to Class 3+ Wind areas constrains the available sites even further 1 MGD Water Cost w/ Wind and Disposal [$/kgal] Estimated prices for using Wind Power Mean: 4.21

53 The energy intensity of desalinating water rises with salinity.

54 Acknowledgements Dr. F. Todd Davidson Dr. Michael Webber
TX General Land Office Mark Adams Andrew Hart TX Water Development Board Sanjeev Kalaswad John Meyer Erika Mancha Environmental Defense Fund Kate Zerrenner


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