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An Examination of the Vulnerability of Groundwater to Climate Change in Olympic Valley Jean E. Moran (California State University East Bay) Michael J. Singleton, Darren Hillegonds, Ate Visser, Brad Esser (Lawrence Livermore National Laboratory)


  1. An Examination of the Vulnerability of Groundwater to Climate Change in Olympic Valley Jean E. Moran (California State University East Bay) Michael J. Singleton, Darren Hillegonds, Ate Visser, Brad Esser (Lawrence Livermore National Laboratory)

  2. Presentation Outline • Predicted effects of climate change on runoff and groundwater • Effects particular to alpine/subalpine (snowmelt dominated) groundwater basins • Dissolved gas and isotopic tools applied • Results from Olympic Valley groundwater basin • Implications for recharge under warmer climate conditions

  3. High Certainty for Earlier Peak Streamflow From: Dettinger et al., 2004

  4. Challenges in predicting effects of climate change on groundwater • Recharge is strongly influenced by changes in precipitation amount, which is not as well- predicted as temperatures – Small changes in precipitation may result in large changes in recharge in semi-arid, arid climates • Downscaling is major issue for predicting GW response • Wide range in subsurface residence times of complicates response of surface water- groundwater interaction • Non-climatic drivers exert large influence on recharge and groundwater levels

  5. Connections between snowmelt and groundwater recharge are poorly understood When and where does recharge take place? What is the residence time of groundwater? Groundwater Age ? 3 H- 3 He, 4 He rad [after Domenico & Schwartz, 1990] Noble Gases Recharge Temperature Excess Air

  6. Climate change effects that are particular to alpine/sub-alpine GW basins • Occur at elevations where change in form of precipitation will be important • Rain on snow events generate flooding events • Down-scaling of GCMs important to capture basin physiography • Disparate recharge mechanisms possible (mountain block/fractured rock, influent streams, diffuse snowmelt)

  7. Tritium decays to 3 He p p n n n p 3 H 3 He Tritium ( 3 H) is an unstable nucleus and ejects an energetic electron to become an atom of helium-3 ( 3 He )

  8. The 3 He from 3 H decay starts to accumulate once the water has become groundwater 0 years 12 years 24 years Age (years) = 18 x ln( 1 + 3 He / 3 H )

  9. Temperature of recharge is determined from noble gas concentrations A reasonable range in pressure (altitude) is assumed and temperatures are calculated from equilibrium solubility component 2.0E-04 (mole/mole, 1 atm) Xenon 1.5E-04 1.0E-04 Krypton Solubility Argon 5.0E-05 Neon Helium 0.0E+00 0 10 20 30 Temperature (C) Analytical uncertainty is approximately +/- 1°C

  10. Excess air concentrations reflect air entrainment and hydrostatic pressure during recharge Artificial recharge and recharge through Little or no vadose zone interaction results in fractures adds a lot of excess air to very low excess air groundwater due to large fluctuations in the water table Recharge via fractures in hard rock terrain would trap a lot of excess air

  11. The Olympic Valley Basin Olympic Valley

  12. Wells Sampled Olympic Valley • 6 production wells • 22 monitoring wells

  13. 3 Stream Flow Gauges 2 Horizontal Wells

  14. Groundwater Ages - Cross Section 2: Mixed bedrock and 1. Shallow alluvial alluvial flow aquifer -Pre-modern -Recent recharge component -Radiogenic 4 He 4 He-rad

  15. Comparing excess air concentrations Singleton and Moran, WRR 2009 1 Manning and Caine, 2007; 2 Cey et al., 2008

  16. • RTs consistent with or slightly higher than MAATs • Mean RT (7.8C) matches monthly mean air temperature for May (7.7C) • Under current conditions, most recharge likely occurs during May-June

  17. • Data from an instrumented soil zone at Gin Flat, Yosemite • Rapid increase in soil temps and SWC once snowpack melts • Nightly freeze allows soil to drain into weathered granite Flint et al., 2008 Vadose Zone J.

  18. Findings: Recharge location and residence time • Recharge occurs on lower slopes of catchment – Recharge temperatures close to mean annual air temperature and higher than expected for direct infiltration of snowmelt – Low excess air – minimal recharge through fractured rock – d 13 C of DIC indicates exchange with soil gas CO 2 • Groundwater (even deep groundwater) in upstream portion of the basin is young

  19. Effects of Climate Change Climate Change Scenarios Effect on Recharge and Discharge • More recharge, if precip rate is • More precip as rain, extended lower than current snowpack melt period of runoff rate • Early decreased baseflow (fast • Earlier runoff drainage) • Increased overland flow, less • More rain on snow events recharge to alluvium • More nights above freezing • More saturation-induced overland flow, less recharge temp. • Less recharge, near immediate effect on GW availability and • Less total precip streamflow Effects will be immediate and drastic at Olympic Valley

  20. Acknowledgements • Squaw Valley Public Services District – Derrik Williams (Hydrometrics LLC) • Friends of Squaw Creek • The Resort at Squaw Creek • Squaw Valley Mutual Water Company • Matt Reeves , Desert Research Institute • Tony Ferenzi, Placer County Water Agency • Students: – C. Cox, C. Tulley, C. Barton, G. Rhett, D. Meyer, H. Bigman , Elizabeth Derubeis • LLNL Labs: – Noble Gas Lab (D. Hillegonds, M. Sharp) – EMRL (R. Bibby, E. Guthrie) – Stable Isotope Lab (S. Roberts) • Funding: LLNL Climate Initiative and SWRCB GAMA program

  21. Comparing three high elevation basins Drainage Max Valley Max Max Average Average Area depth to floor elevation discharge annual Annual bedrock elevation in during discharge Precip GW Basin drainage study Area Olympic 22 km 2 55m 1898m – 2750m 5.2 m 3 /s 2x10 7 1016- m 3 /yr Valley 1853m 1650 mm 2.6 km 2 Yosemite 465 km 2 600m 1224m – 3997m 235 m 3 /s 64 x10 7 1277 mm m 3 /yr Valley (mean 1100m 300m) (540m) 31 km 2 433 km 2 28 m 3 /s 50x10 7 Martis 320 m 1737m- 2624m 584-1910 m 3 /yr Valley 1798m mm 142 km 2

  22. Squaw Creek Gauging Stations • Fed by two major tributaries • Very low flow in the fall • Gaining along the valley reach

  23. Carbon isotopes are consistent with the incorporation of soil CO 2 during recharge

  24. What is excess air ? Air bubbles can be trapped during recharge and subsequently dissolve because of the increased pressure

  25. Components of dissolved noble gases • Equilibrium solubility (dependent upon p, T) 250% Tritiogenic 3 He • Excess Air Percent equilibrium saturation Terrigenic He • Mantle Helium • Terrigenic Helium 150% Excess Air • Tritiogenic helium (for 3 H- 3 He age) 50% 3He 4He Ne Ar Kr Xe

  26. Martis Valley sample locations Martis Valley • 17 wells and 4 surface water locations sampled in Dec/Jan • Most field work will take place this summer

  27. Fraction pre-modern

  28. Older groundwater is captured by wells during late summer 30 SVPSD Well 1 25 SVPSD Well 2 Apparent Age (yrs) SVPSD Well 3 20 SVPSD Well 5 MWC Well 1 15 MWC Well 2 10 5 0 -5 Sampling Date

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