Suitability for Managed Aquifer Recharge (MAR)
Transcription
Suitability for Managed Aquifer Recharge (MAR)
Suitability for Managed Aquifer Recharge (MAR) Projects within the Pajaro Valley: Update on GIS Analysis and Percolation Evaluation for MAR potential T. Russo1, A. T. Fisher1, M. Los Huertos2, N. Jacuzzi2 1 University of California, Santa Cruz 2 California State University, Monterey Bay Community Dialog #5 Water in the Pajaro Valley 12 July 2011 Watsonville Civic Center Estimating the suitability for MAR using a geographic information system (GIS) MAR Google maps • Surface physical data • Subsurface geology and hydrogeology • Potential access to a water supply Estimating the suitability for MAR using a geographic information system (GIS) MAR Google maps • Surface physical data • Subsurface geology and hydrogeology • Potential access to a water supply (underway) Surface analysis Relative MAR suitability Preliminary Map based on: Soil classification, topography, land use and bedrock geology High MAR suitability Low MAR suitability Subsurface analysis Relative recharge suitability Preliminary Map based on: Calculated aquifer transmissivity and presence of clay confining layers High MAR suitability Low MAR suitability Next steps for GIS analysis • Integrate subsurface and surface analyses • Complete (physical) analysis of potential water sources (not political, regulatory, legal) • Revise analyses of surface data based on feedback, site specific information, limited field testing • Make "final" data product available for use by stakeholders in digital form • Target date for completion of GIS study: 1-2 months Nested Approach for Implementation • GIS analysis is intended to help identify MAR sites …but… • Spatial data may be inaccurate in some locations; • Establishing pilot field studies is expensive and can be technically challenging, …so… • We designed a 3–10 day percolation testing system to test sites that have potential for MAR Field testing of infiltration potential for MAR • Small, multi-day percolation tests, 0.1 to 10 m2 • Scale up at successful sites • Monitor infiltration rate • Expand to additional sites • Initial support secured from SCC-RCD, NSF Graduate Fellowship, and by re-scoping funds previously secured from NIWR Solar panels Large volume tank Top off fitting Float valve 24V R/V pump 75–200' hose Deep cycle batteries Heavy duty trailer Power regulator, data logger Solinoid Flow meter Test pit (0.1 –10 m2) Float valve 3 test sites Survey image from USDA-NRCS, 2010 Infiltration Capacity, Bokariza-Drobac, Middle pit Infiltration rate (ft/day) 80.0 70.0 60.0 50.0 ~20 ft/day 40.0 30.0 20.0 10.0 0.0 0.0 1.0 2.0 Time (day) 3.0 4.0 5.0 Infiltration rate (ft/day) Infiltration rate (ft/day) 120 Bokariza-Drobac, Northern pit Preliminary 100 80 ~40 ft/day 60 40 20 0 0.00 0.05 0.10 Time (day) 0.15 0.20 Bokariza-Drobac, Southern pit Preliminary 12 10 ~6 ft/day 8 6 4 2 0 0.02 0.04 0.06 0.08 Time (day) 0.10 0.12 ~20-40 ft/day ~6 ft/day Survey image from USDA-NRCS, 2010 Next steps… • Integration of GIS maps • Continue percolation testing - Additional tests at Bokariza-Drobac - New sites • Modification of the PVWMA-USGS groundwater model Many thanks for collaboration, advice… Maria Osiadacz, Brian Lockwood, Mike Cloud, Jonathan Lear, Randy Hanson, Noah Finnegan …and for support that helps to make this work possible… Questions?