1 2 3 4 5 Draft (ver. 2) Groundwater Information for Elkhorn Slough Greg Shellenbarger (gshellen@usgs.gov) Groundwater – Background 6 7 Elkhorn Slough occupies a small portion of the southern end of the Pajaro Valley 8 groundwater basin. Groundwater recharge in this basin comes primarily from 9 precipitation, applied water use (e.g., agricultural irrigation) and stream recharge. 10 Groundwater is extracted predominately for urban, agricultural and rural residential use. 11 This basin has been subject to severe groundwater overdrafts (where extraction exceeds 12 recharge) for over 60 years (CDWR 2004). Annual estimates of groundwater extractions 13 (~69,000 acre feet) exceed recharge (~61,000 af) by less than 10,000 af but are almost 14 three times the sustainable extraction estimate of 24,000 af (RMC 2001 as cited in 15 CDWR 2004). The severe, chronic overdrafts have led to falling groundwater levels and 16 significant seawater intrusion along the coastal margin for this basin. Overdrafts appear 17 to be affecting primarily the confined aquifers at 180’ and 400’ (this is true for the 18 Salinas Valley groundwater basin – I have not yet found aquifer depths for Pajaro 19 Valley). Rainwater recharge though the porous coastal sand dunes may serve as a 20 hydraulic barrier to seawater intrusion in the shallower aquifers (CDWR 2004). 21 22 Potential Subsidence Due to Groundwater Pumping 23 (requires analysis of an existing dataset) 24 25 In areas that experience seasonal groundwater withdrawals and recharge (i.e., each 26 process happens during a different season), reversible seasonal uplift and subsidence of 27 the soil can occur (Bawden et al. 2003). Continued extraction of groundwater at a rate 28 that exceeds the recharge rate can lead to regional (on the scale of km to 10s of km) 29 ground compaction around wells. The issue of subsidence is a critical one when 30 evaluating land elevations in a tidal system. Marsh development and growth requires a 31 very narrow range in elevation to provide a proper wetting period for survival (Cornu and 32 Sadro 2002). 33 Relatively recently, a technique has been developed that enables high resolution 34 detection of changes in land surface elevations on a seasonal scale using satellite 35 Interferometric Synthetic Aperture Radar (InSAR). By bouncing radar signals off the 36 ground at different times but from the same point in space, millimeter-scale accuracy of 37 the ground surface elevation changes can be determined (Galloway et al. 1998). 38 Interferograms have been developed to show subsidence resulting from groundwater 39 pumping, hydrocarbon production and a variety of other anthropogenic activities that 40 contribute to uplift and subsidence (Bawden et al. 2003). 41 The USGS has about 16 pairs of InSAR images from Elkhorn Slough collected 42 between 1996 and 2000. These image pairs are currently unprocessed and of unknown 43 quality, but presumably some pairs may be useful to determine seasonal (and perhaps 44 interannual) changes in land surface elevation. The image pairs predominately cover 45 transitions between summer and winter, so it might only be possible to determine 46 seasonal uplift and infer subsidence. 47 48 Tidally Pumped and Terrestrially Derived Groundwater flux 49 50 In the coastal region, groundwater discharge along the ocean or an estuary margin 51 rarely consists solely of freshwater. Rather, the near-coast subsurface serves as a reaction 52 zone of fresher groundwater and more saline seawater that has been termed a 53 ‘subterranean estuary’ (Moore 1999). The water in the subterranean estuary has been 54 called submarine groundwater (SGW) to emphasize, that it is not only fresh groundwater, 55 but can include a significant component of seawater that infiltrates into the subsurface. 56 This water can then be subsequently discharged to the coast with changed chemical 57 characteristics (Burnett et al. 2002). 58 Even in the absence of fresh groundwater, SGW discharge can be explained by the 59 physics of the interaction of the waves and tide with the shoreline (Nielsen 1990; Horn 60 2002). The face of the estuary margin acts like a highly non-linear filter to the movement 61 of water across it. Because of the non-linearity, a tidally averaged over-height of the 62 water in the ground relative to the coast can be maintained. This over-height implies that 63 tidal physics alone can always provide a hydraulic gradient in the shallow unconfined 64 aquifer that drives water from the ground to the sea. The groundwater over-height is 65 increased further with the presence of waves (Li et al. 1999). 66 In 2002, a group from Stanford University initiated a study to estimate groundwater 67 fluxes into Elkhorn Slough using radium isotopes (Misra and Paytan 2002). Naturally 68 occurring radium isotopes are bound to soil particles in freshwater but readily desorb via 69 ion exchange when in contact with solutions of higher ionic strength (desorption begins 70 at salinities around 2 and is complete at salinities around 20). Preliminary results show 71 higher radium activities at low tide compared to high tide. This is consistent with the 72 above explanation of the dynamics of tides and waves on the shallow unconfined aquifer 73 near the shoreline. In addition, the data suggest that there is potentially fresh 74 groundwater inputs along the northern reaches of Elkhorn Slough (north of the end of the 75 deep channel), although the flux of this groundwater to the slough has not been 76 quantified. Supporting data collected from the Elkhorn Slough region also suggest likely 77 groundwater fluxes (not quantified) into the Salinas River and/or Moro Cojo Slough. 78 79 Literature Cited 80 81 82 83 Bawden, G.W., M. Sneed, S.V. Stork, and D.L. Galloway. 2003. Measuring humaninduced land subsidence from space. U.S. Geological Survey Fact Sheet 069-03, 4p. Burnett, W., J.P. Chanton, J. Christoff, E. Kontar, S. Krupa, M. Lambert, W.S. Moore, D. 84 O’Rourke, R. Paulsen, C. Smith, L. Smith, and M. Taniguchi. 2002. Assessing 85 methodologies for measuring groundwater discharge to the ocean. EOS, Trans. 86 AGU, 83: 117-123. 87 California Department of Water Resources. 2004. Central coast hydrologic region, 88 Pajaro Valley groundwater basin, California’s Groundwater Bulletin 118. 89 http://www.dpla2.water.ca.gov/publications/groundwater/bulletin118/basins/pdfs_des 90 c/3-2.pdf 91 Cornu, C.E., and S. Sadro. 2002. Physical and functional responses to experimental 92 marsh surface elevation manipulation in Coos Bay’s South Slough. Restoration 93 Ecology, 10(3): 474-486. 94 Galloway, D.L., K.W. Hudnut, S.E. Ingebritsen, S.P. Phillips, G. Peltzer, F. Rogez, and 95 P.A. Rosen. 1998. Detection of aquifer system compaction and land subsidence 96 using inferometric synthetic aperture radar, Antelope Valley, Mojave Desert, 97 California. Water Resources Research, 34: 2573-2585. 98 Horn, D.P. 2002. Beach groundwater dynamics. Geomorph., 48: 121-146. 99 Li, L., D.A. Barry, F. Stagnitti, and J.-P. Parlange. 1999. Submarine groundwater 100 discharge and associated chemical input to a coastal sea. Water Resour. Res., 35: 101 3253-3259. 102 Misra, G., and A. Paytan. 2002. Radium isotopes as tracers for groundwater input in 103 Elkhorn Slough, California. American Geophysical Union, Fall Meeting 2002, 104 abstract #OS22B-0276. 105 106 107 108 109 110 111 112 Moore, W.S. 1999. The subterranean estuary: a reaction zone of groundwater and seawater. Marine Chemistry, 65: 111-126. Nielsen, P. 1990. Tidal dynamics of the water table in beaches. Water Resources Res., 26(9): 2127-2134. Raines, Melton, and Carella. 2001. Pajaro Valley Water Management Agency – Revised Basin Management Plan (Draft).