Ground Water Basin Framework Project Final Report

Prepared by:

121 S. Jackson St. Moscow, ID 83843 Web Site: www.terragraphics.com

And

Ralston Hydrologic Services 1122 E. B St. Moscow, ID 83843

January 31, 2011

Palouse Ground Water Basin Framework Project FINAL report

ii

Palouse Ground Water Basin Framework Project Final Report

Prepared for:

1300 NE Henley Ct., #6 Pullman, WA 99163

Grant G1000293 between the Washington Department of Ecology and the Palouse Conservation District

Prepared by: TerraGraphics Environmental Engineering, Inc. 121 S. Jackson St. Moscow, ID 83843 www.terragraphics.com

and

Ralston Hydrologic Services 1122 E. B St. Moscow, ID 83843

January 31, 2011

Palouse Ground Water Basin Framework Project FINAL report

Table of Contents

Executive Summary...... xiv Section 1.0 Introduction ...... 1 1.1 Purpose and Objectives...... 1 Section 2.0 Task 2 – Compilation ...... 5 2.1 Collection...... 5 2.1.1 Documents Included ...... 5 2.1.2 Documents Excluded ...... 5 2.1.3 Search Locations...... 5 2.1.4 Related Documents Not Found...... 6 2.2 Compilation ...... 6 2.2.1 Electronic Copies of Documents...... 6 2.2.2 Collection of Information ...... 7 2.3 Database Organization...... 10 2.3.1 Database - Tables...... 11 2.3.2 Database - Forms ...... 11 2.3.3 Database - Queries ...... 11 2.3.4 Database - Reports ...... 12 2.3.5 Database User ...... 12 2.4 Quality Assurance/Quality Control ...... 12 Section 3.0 Task 3 – Synthesis...... 17 3.1 Introduction...... 17 3.2 Geologic Framework ...... 17 3.2.1 Introduction...... 17 3.2.2 Geologic Nomenclature ...... 18 3.2.3 Regional Geologic Characteristics...... 18 3.2.4 Palouse Basin Geologic Characteristics...... 19 3.2.4.1 Pullman-Moscow Subarea ...... 19 3.2.4.2 Northern Subarea ...... 21 3.2.4.3 Western Subarea ...... 22 3.2.5 Description of Stratigraphic and Structural Features...... 22 3.2.5.1 Crystalline Basement Rocks ...... 22 3.2.5.2 Imnaha Formation...... 24 3.2.5.3 Grande Ronde Formation...... 24 3.2.5.4 Wanapum Formation ...... 26 3.2.5.5 Saddle Mountains Formation...... 26 3.2.5.6 Structural Features ...... 27 3.3 Hydrogeologic Framework...... 28 3.3.1 Introduction...... 28 3.3.2 Aquifer Identification and Temporal Growth of Knowledge ...... 28 3.3.2.1 Aquifer Identification...... 28 3.3.2.2 Temporal Growth of Knowledge of the Aquifers...... 30

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Palouse Ground Water Basin Framework Project FINAL report

3.3.3 Characteristics of the Lower Aquifer...... 33 3.3.3.1 Water-Producing Zones ...... 34 3.3.3.2 Hydraulic Characteristics...... 35 3.3.3.3 Aquifer Boundaries...... 38 3.3.3.4 Horizontal and Vertical Hydraulic Gradients ...... 40 3.3.3.5 Temporal Water-Level Changes...... 40 3.3.4 Characteristics of the Upper Aquifer ...... 42 3.3.4.1 Water Producing Zones...... 42 3.3.4.2 Hydraulic Characteristics...... 42 3.3.4.3 Aquifer Boundaries...... 43 3.3.4.4 Horizontal and Vertical Hydraulic Gradients ...... 43 3.3.4.5 Temporal Water-Level Changes...... 43 3.3.5 Ground-Water Flow Systems...... 43 3.3.5.1 General Flow System Theory ...... 43 3.3.5.2 Ground-Water Flow Systems in the Palouse Basin ...... 44 3.4 Water Balance...... 45 3.4.1 Introduction...... 45 3.4.2 Surface Water Gain/Loss ...... 46 3.4.3 Surface Sediment Water Balance...... 49 3.4.3.1 Ground-Water Recharge ...... 49 3.4.3.2 Ground-water Discharge...... 54 3.4.3.3 Change in Storage...... 54 3.4.4 Upper Aquifer Water Balance...... 54 3.4.4.1 Ground-Water Recharge ...... 55 3.4.4.2 Ground-Water Discharge...... 56 3.4.4.3 Change in Storage...... 57 3.4.5 Lower Aquifer Water Balance ...... 58 3.4.5.1 Ground-Water Recharge ...... 58 3.4.5.2 Ground-Water Discharge...... 59 3.4.5.3 Change in Storage...... 60 3.4.6 Ground-Water Isotope Analysis ...... 60 3.5 Numerical Models...... 63 3.5.1 Introduction...... 63 3.5.2 Barker (1979) Model...... 64 3.5.2.1 Model Boundaries...... 64 3.5.2.2 Representation of the Aquifers ...... 65 3.5.2.3 Representation of the Recharge to the Aquifers ...... 65 3.5.2.4 Representation of Discharge from the Aquifer...... 66 3.5.2.5 Predicted Relationship of Pumping to Water-Level Decline...... 66 3.5.2.6 Water-Budget Analysis...... 67 3.5.2.7 Recommendations...... 68 3.5.3 Lum et al. (1990) Model ...... 68 3.5.3.1 Model Boundaries...... 69 3.5.3.2 Representation of the Aquifers ...... 70 3.5.3.3 Representation of Recharge to the Aquifers ...... 70 3.5.3.4 Representation of Discharge from the Aquifers ...... 71

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Palouse Ground Water Basin Framework Project FINAL report

3.5.3.5 Model Calibration ...... 71 3.5.3.6 Predicted Relationship of Pumping to Water-Level Decline...... 72 3.5.3.7 Water-Budget Analysis...... 73 3.5.3.8 Recommendation ...... 73 3.5.4 Post Lum et al. (1990) Model Analysis ...... 74 3.5.4.1 Brown (1991) Analysis...... 74 3.5.4.2 Johnson et al. (1996) Analysis...... 74 3.5.5 Comparison of Field Data to Numerical Model Predictions...... 74 3.5.5.1 Summary of Barker (1979) Model Predictions...... 74 3.5.5.2 Summary of Lum et al. (1990) Model Predictions ...... 75 3.5.5.3 Summary of Historical Pumping Rates and Water-Level Decline ...... 76 3.5.5.4 Comparison of Barker (1979) Numerical Model Predictions to Field Data...... 76 3.5.5.5 Comparison of Lum et al. (1990) Numerical Model Predictions to Field Data ... 77 3.5.5.6 Discussion of Model Results ...... 77 Section 4.0 Task 4.5 – Preliminary Data-Gap Investigation: Mass-Water Level Measurements ...... 172 4.1 Introduction...... 172 4.2 Selection of Study Area ...... 172 4.3 Selection of Target Wells ...... 172 4.4 Review of List of Target Wells...... 173 4.5 Field Measurement Project Plan...... 173 4.6 Field Results ...... 174 4.6.1 Well 14N/44E-02M01 ...... 174 4.6.2 Well 14N/44E-03P01...... 174 4.6.3 Well 14N/44E-05F01...... 174 4.6.4 Well 14N/44E-10B01 ...... 174 4.6.5 Well 14N/44E-10B02 ...... 175 4.6.6 Well 14N/44E-16P01 LE12...... 175 4.6.7 Well 14N/44E-24J01 ...... 175 4.6.8 Well 15N/44E-05A01 ...... 175 4.6.9 Well 15N/44E-19B01 ...... 176 4.6.10 Well 15N/44E-21C01 ...... 176 4.6.11 Well 15N/44E-26L01...... 176 4.6.12 Well 15N/44E-33B01 ...... 176 4.6.13 Well 15N/44E-35E01...... 176 4.6.14 Additional wells measured...... 177 4.7 Discussion...... 177 4.7.1 Bottom-Hole Elevation ...... 177 4.7.2 Water-Level Elevation Versus Bottom-Hole Elevation...... 178 4.7.3 Water-Level Elevation Versus Time...... 179 4.7.4 Rates of Water-Level Decline...... 180 4.7.5 Comparison to the Barker (1979) Study ...... 180 4.8 Conclusions...... 180 4.9 Recommendations...... 181

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Palouse Ground Water Basin Framework Project FINAL report

Section 5.0 Task 4.5 – Preliminary Data-Gap Investigation: Surface-Water / Ground-Water Interaction ...... 205 5.1 Introduction...... 205 5.2 Hydrogeologic Conceptual Model of a Losing Stream ...... 205 5.3 South Fork of the Palouse River in Pullman Relative to the Lower Aquifer ...... 207 5.3.1 Hydrogeologic Setting ...... 207 5.3.2 Hydrograph Analysis ...... 207 5.4 Palouse River in the City of Palouse Relative to the Lower Aquifer ...... 209 5.4.1 Hydrogeologic Setting ...... 209 5.4.2 Hydrograph Analysis ...... 209 5.4.3 Aquifer Water-Temperature Analysis...... 209 5.5 Paradise Creek in Moscow Relative to the Upper Aquifer...... 211 5.5.1 Hydrogeologic Setting ...... 211 5.5.2 Hydrograph Analysis for High Flow Events in Paradise Creek ...... 211 5.5.3 Hydrograph Analysis for Low Flow Events in Paradise Creek...... 212 5.6 Union Flat Creek at Klemgard Park Relative to a Well Completed in Basalt of the Grande Ronde Formation ...... 212 5.6.1 Hydrogeologic Setting ...... 212 5.6.2 Hydrograph Analysis for High Flow Events at the Klemgard Park Site ...... 213 5.7 Conclusions...... 213 Section 6.0 Task 4 – Data-Gap Investigation...... 237 6.1 Introduction...... 237 6.2 Delineation of Data Gaps...... 237 6.2.1 High-Priority Data Gaps ...... 238 6.2.1.1 Hydrogeology West of Pullman...... 238 6.2.1.2 Surface-Water / Ground-Water Interaction Northwest of Pullman ...... 238 6.2.1.3 Maximizing Upper-Aquifer Pumping in the Pullman-Moscow Subarea ...... 238 6.2.2 Medium-Priority Data Gaps...... 238 6.2.2.1 Ground-Water Monitoring Program ...... 238 6.2.2.2 Lower-Aquifer Continuity in the Kamiak Butte to Angel Butte Gap...... 239 6.2.2.3 Hydraulic Sub-basins Within the Pullman-Moscow Subarea...... 239 6.2.2.4 Relationship Between Pumping and Water-Level Decline ...... 239 6.2.2.5 Well-Log Database ...... 239 6.2.3 Low-Priority Data Gaps...... 239 6.2.3.1 Ground-Water Conditions in the Colton, Uniontown, and Genesee Areas ...... 239 6.2.3.2 Ground-Water Conditions in the Garfield Area...... 240 6.2.3.3 Ground-Water Conditions in the Colfax Area...... 240 6.2.3.4 Surface-Water / Ground-Water Interaction Near Colfax...... 240 6.3 Details of High-Priority Data Gaps ...... 240 6.3.1 Hydrogeology West of Pullman...... 240 6.3.1.1 Purpose and Objective ...... 240 6.3.1.2 Proposed Project Location ...... 241 6.3.1.3 Project Description...... 241 6.3.1.4 Project Cost Estimate...... 242 6.3.2 Surface-Water / Ground-Water Interaction Northwest of Pullman ...... 243

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Palouse Ground Water Basin Framework Project FINAL report

6.3.2.1 Purpose and Objectives...... 243 6.3.2.2 Proposed Project Location ...... 244 6.3.2.3 Project Description...... 244 6.3.2.4 Project Cost Estimate...... 245 6.3.3 Maximizing Upper Aquifer Pumping in the Pullman-Moscow Subarea...... 245 6.3.3.1 Purpose and Objectives...... 245 6.3.3.2 Proposed Project Location ...... 246 6.3.3.3 Project Description...... 246 6.3.3.4 Project Cost Estimate...... 246 6.4 Details of Medium-Priority Data Gaps...... 247 6.4.1 Ground-Water Monitoring Program ...... 247 6.4.1.1 Purpose and Objectives...... 247 6.4.1.2 Proposed Project Location ...... 247 6.4.1.3 Project Description...... 247 6.4.1.4 Project Cost Estimate...... 248 6.4.2 Lower-Aquifer Continuity in the Kamiak Butte to Angel Butte Gap...... 248 6.4.2.1 Purpose and Objectives...... 248 6.4.2.2 Proposed Project Location ...... 248 6.4.2.3 Project Description...... 248 6.4.2.4 Project Cost Estimate...... 249 6.4.3 Hydraulic Sub-Basins Within the Pullman-Moscow Subarea ...... 249 6.4.3.1 Purpose and Objective ...... 249 6.4.3.2 Proposed Project Location ...... 249 6.4.3.3 Project Description...... 249 6.4.3.4 Project Cost Estimate...... 250 6.4.4 Relationship Between Pumping and Water-Level Decline ...... 250 6.4.4.1 Purpose and Objectives...... 250 6.4.4.2 Proposed Project Location ...... 250 6.4.4.3 Project Description...... 250 6.4.4.4 Project Cost Estimate...... 250 6.4.5 Well-Log Database ...... 251 6.4.5.1 Purpose and Objectives...... 251 6.4.5.2 Proposed Project Location ...... 251 6.4.5.3 Project Description...... 251 6.4.5.4 Project Cost Estimate...... 252 6.5 Summary and Conclusions ...... 252 Section 7.0 Task 5 – Conclusions and Recommendations...... 264 7.1 Conclusions...... 264 7.1.1 General Conclusions ...... 264 7.1.2 Specific Conclusions...... 265 7.2 Recommendations...... 266 Section 8.0 List of References...... 267

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Palouse Ground Water Basin Framework Project FINAL report

List of Figures Figure 1-1 Current boundary of the Palouse Ground Water Basin...... 4 Figure 2-1 Print screen of the Tables object within the database...... 14 Figure 2-2 Table relationships as depicted by Microsoft Access...... 14 Figure 2-3 Print screen of the Forms object within the database...... 15 Figure 2-4 Print screen of the Queries object within the database...... 15 Figure 2-5 Print screen of the Reports object within the database...... 16 Figure 3-1 Generalized geologic map of the Palouse Basin showing subareas (from Bush, 2005d)...... 80 Figure 3-2 Map of area covered by the Columbia River basalts (from Hooper, 1982)...... 81 Figure 3-3 Stratigraphic units of the Columbia River Basalt Group in the Palouse Basin (from Bush, 2008)...... 82 Figure 3-4 Altitude of the top of crystalline basement rocks (from Lum et al., 1990)...... 83 Figure 3-5 Emplacement of R1 of the Grande Ronde basalt (from Bush, 2005d)...... 84 Figure 3-6 Emplacement of N1 of the Grande Ronde basalt (from Bush, 2005d)...... 85 Figure 3-7 Emplacement of R2 of the Grande Ronde basalt (from Bush, 2005d)...... 86 Figure 3-8 Emplacement of N2 of the Grande Ronde basalt (from Bush, 2005d)...... 87 Figure 3-9 Emplacement of Roza Member of the Wanapum basalt (from Bush, 2005d)...... 88 Figure 3-10 Emplacement of Priest Rapids Member of the Wanapum basalt (from Bush, 2006b)...... 89 Figure 3-11a East-west geologic cross section (from Bush and Garwood, 2005f)...... 90 Figure 3-11b East-west geologic cross section (from Bush and Garwood, 2005f)...... 91 Figure 3-12 Panel diagram of the Palouse Basin (from Bush and Garwood, 2005h)...... 92 Figure 3-13 Geologic cross section through IDWR (Moscow) Well #4 (from Bush, 2006a)...... 93 Figure 3-14 Geologic cross section through Pullman Well #7 (from Bush et al., 2001a)...... 94 Figure 3-15a Stratigraphy of the Pullman – Moscow area (from Conrey and Wolff, 2010)...... 95 Figure 3-15b Stratigraphy and geologic cross section of the Pullman – Moscow area (from Conrey and Wolff, 2010)...... 96 Figure 3-16 Locations of cross sections in the Northern and Western subareas (from Bush and Garwood, 2005f)...... 97 Figure 3-17 Cross sections A-A’ and G-G’ in the Northern subarea (from Bush and Garwood, 2005f). .98 Figure 3-18 Cross sections E-E’ and F-F’ in the Western subarea (from Bush and Garwood, 2005f)...... 99 Figure 3-19 Cross section from Pullman to Colfax (from Leek, 2006)...... 100 Figure 3-20a Preliminary structural contour map on the upper Grande Ronde surface; focus on Pullman – Moscow Subarea (from Bush and Garwood, 2005j)...... 101 Figure 3-20b Preliminary structural contour map on the upper Grande Ronde surface (from Bush and Garwood, 2005j)...... 102 Figure 3-21 Map showing depth to the top of the Grande Ronde Formation (from Robischon, 2010a). 103 Figure 3-22a Location map showing production wells in the Palouse Basin...... 104 Figure 3-22b Well lithology and construction information on wells within the Pullman-Moscow subarea (from Fiedler, 2009)...... 105 Figure 3-23 Water-level elevation data for the lower aquifer in the Pullman – Moscow subarea (from Barker, 1979)...... 106

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Palouse Ground Water Basin Framework Project FINAL report

Figure 3-24 Plot of altitude of water level plotted versus altitude of the bottom of the well for wells in the Pullman – Moscow subarea (from Barker, 1979)...... 107 Figure 3-25 Hydrograph for WSU test well (Robischon, personal communication, 2010)...... 108 Figure 3-26 Hydrographs for wells completed in the loess, upper aquifer (Wanapum aquifer), and lower aquifer (Grande Ronde aquifer) in the Pullman – Moscow subarea (from Leek, 2006)...... 109 Figure 3-27 Hydrographs for wells completed in the lower aquifer in Pullman and Palouse (from PBAC, 2001) ...... 110 Figure 3-28 Assumed water-level elevation map of the upper aquifer prior to development (from Barker, 1979)...... 111 Figure 3-29a Map locations for springs, wells, streamflow gaging stations, and in-stream piezometers along the South Fork of the Palouse River and Paradise Creek (from Sinclair et al., 2009)...... 112 Figure 3-29b Darcy flux estimates of potential streamflow gains and losses along Paradise Creek and the south Fork Palouse River, by seepage reach and river mile, for August 14-17, 2006 (from Sinclair et al., 2009)...... 113 Figure 3-30 Map locations for springs, wells, streamflow gaging stations, and instream piezometers along the Palouse River (from Sinclair et al., 2009)...... 114 Figure 3-31 Roza/Priest Rapids contact relative to ground-water discharge zones (from Heinemann, 1994)...... 115 Figure 3-32 Estimated recharge distribution for predevelopment land-use conditions for the modeled zones imposed on the ground-water model grid system (from Bauer and Vaccaro, 1990)...... 116 Figure 3-33 Estimated recharge distribution for current land-use conditions for the modeled zones imposed on the ground-water model grid system (from Bauer and Vaccaro, 1990)...... 117 Figure 3-34 Digital elevation model of part of the Palouse Basin and its location in the Pacific Northwest (from O’Geen et al., 2005)...... 118 Figure 3-35 Spatial representation of recharge rates for major hydrostratigraphic units identified from the SSURGO database (from O’Geen, 2005)...... 119 Figure 3-36 Location maps of core holes drilled for the Fairly et al. (2006) study...... 120 Figure 3-37 Plot of average yearly water level decline in USGS observation well versus average yearly pumpage from upper aquifer for 5 year moving periods, 1955-1987 (from Baines, 1992)...... 121 Figure 3-38 Static water level elevations for the upper and lower aquifers (from Robischon, personal communication, 2010) ...... 122 Figure 3-39 Combined yearly pumpage from upper aquifer, Moscow and University of (from Baines, 1992)...... 123 Figure 3-40 Locations for measured municipal and private wells in the Viola and Moscow West quadrangles (from Provant, 1995)...... 124 Figure 3-41 Change in water-level between August 1994 and January 1995 for wells completed in the upper aquifer (from Provant, 1995)...... 125 Figure 3-42 Long-term change in water-level between August 1994 and measurements conducted in 1955, 1964, 1972, and 1975 (from Provant, 1995)...... 126 Figure 3-43 Graph of upper aquifer (i.e. Wanapum) pumping rates and water level data in Moscow well #2 and the USGS well from 1938 to 2009 (from Robischon, personal communication, 2010)...... 127 Figure 3-44 Isopach map of overburden thickness in the Palouse Basin showing lower aquifer sampling points (from Douglas, 2004)...... 128 Figure 3-45 Discharge from the lower aquifer and the voluntary 1% annual increase target, 4 major entities combined (from PBAC, 2009c)...... 129

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Palouse Ground Water Basin Framework Project FINAL report

Figure 3-46 Geographic distribution of 18O values in groundwater samples for the Larson (1997) analysis (from Larson, 1997)...... 130 Figure 3-47 Arithmetic plot of 14C concentration versus elevation of the producing zone for ground water samples collected from the lower aquifer (Grande Ronde) and upper aquifer (Wanapum) systems (from Douglas, 2004)...... 131 Figure 3-48 Shaded-cell map of ground water carbon-14 (pmc) concentrations in the lower aquifer system (from Douglas, 2004)...... 132 Figure 3-49 Location map for the Barker (1979) numerical model...... 133 Figure 3-50 Boundary identification map for the Barker (1979) numerical model...... 134 Figure 3-51 Calibrated transmissivity map for the Barker (1979) numerical model...... 135 Figure 3-52 Confining layer thickness map for the Barker (1979) numerical model...... 136 Figure 3-53 Differences between model predicted and assumed pre-development water levels for the Barker (1979) numerical model...... 137 Figure 3-54 Comparison of model predicted and measured water levels in 1975 for the Barker (1979) numerical model...... 138 Figure 3-55 Comparison of model predicted and measured water levels for selected wells for the Barker (1979) numerical model...... 139 Figure 3-56 Predevelopment water-level and water budget map for the Barker (1979) numerical model (flow in acre-feet per year)...... 140 Figure 3-57 Model predicted pre-development vertical leakage map for the Barker (1979) numerical model...... 141 Figure 3-58 Model predicted 1975 water-level and water budget map for the Barker (1979) numerical model (flow in acre-feet per year)...... 142 Figure 3-59 Model predicted 1975 vertical leakage map for the Barker (1979) numerical model...... 143 Figure 3-60 Model predicted recharge and discharge changes for the Barker (1979) numerical model. 144 Figure 3-61 Model predicted water-level declines at the 1971-1975 average pumping rate of 6,600 acre- feet/year for selected wells for the Barker (1979) numerical model...... 145 Figure 3-62 Model predicted water-level declines in from 1975 to 2000 if the 1971-1975 average pumping rate is doubled between 1976 and 1999 for the Barker (1979) numerical model...... 146 Figure 3-63 Model predicted water-level declines in from 1975 to 2000 if the 1971-1975 average pumping rate is tripled between 1976-1999 for the Barker (1979) numerical model...... 147 Figure 3-64 Comparison of boundaries and hydraulic coefficients for the Barker (1979) and Lum et al. (1990) numerical models...... 148 Figure 3-65 Depiction of the model layers for the Lum et al. (1990) numerical model...... 149 Figure 3-66 Delineation of boundary conditions and areal distribution of recharge to the loess for predevelopment (left) and for current conditions (right) for the Lum et al. (1990) numerical model...... 150 Figure 3-67 Model grid and cell explanations for the upper aquifer (Wanapum) layer of the Lum et al. (1990) numerical model...... 151 Figure 3-68 Model grid and cell explanations for the lower aquifer (Grande Ronde) layer of the Lum et al. (1990) numerical model...... 152 Figure 3-69 Location and configuration of cross sectional models for the Lum et al. (1990) numerical model...... 153 Figure 3-70 Horizontal hydraulic conductivity and the ratio of horizontal to vertical hydraulic conductivity for the Lum et al. (1990) numerical model...... 154

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Palouse Ground Water Basin Framework Project FINAL report

Figure 3-71 Calibrated water-level elevations for the time averaged period of 1974 – 1985 for the Lum et al. (1990) numerical model...... 155 Figure 3-72 Comparison of observed and simulated water levels in wells for the Lum et al. (1990) numerical model...... 156 Figure 3-73 Simulated water levels in Pullman and Moscow from the Lum et al. (1990) numerical model...... 157 Figure 3-74 Schematic of recharge and discharge to each layer of the Lum et al. (1990) numerical model (taken from Johnson et al., 1996)...... 158 Figure 4-1 Barrier zone as postulated by Barker (1979)...... 183 Figure 4-2 Wells targeted for water-level measurement program in summer 2010...... 184 Figure 4-3 Graph of water-level elevations for the period of record in wells believed to be located in the upper aquifer. Well 14N/44E-10B01 may be in the lower aquifer...... 185 Figure 4-4 Graph of water-level elevations for the period of record in well 14N/44E-05F01. Well is believed to be located in the lower aquifer but the scale is far below other upper aquifer wells. Elevation scale is still 200 feet...... 186 Figure 4-5 Graph of water-level elevations for the period of record in wells believed to be located in the lower aquifer...... 187 Figure 4-6 Bottom-hole elevations for all proposed wells overlain on the Bush and Garwood (2005j) structural contour map of the top of the Grande Ronde Formation...... 188 Figure 4-7 Graph of water-level elevation (measured in 2009 or 2010) versus bottom-hole elevation. .189 Figure 4-8 Map of water-elevation data collected in 2009 found in Synder and Haynes (2010) and 2010 for this program...... 190 Figure 4-9 Graph of water-level elevation versus time...... 191 Figure 4-10 Map of feet of water-level decline per number of years based on range of water-level measurements, most recently in 2010...... 192 Figure 4-11 Map of rate of water-level decline based on the two most recent water level measurements...... 193 Figure 5-1 Map showing the working boundary for the Palouse Ground Water Basin and study sites for surface-water/ground-water interaction investigation...... 216 Figure 5-2 Comparison of Spokane River stage and water levels in selected wells completed in the Spokane Valley/Rathdrum Prairie Aquifer (Caldwell and Bowers, 2003)...... 217 Figure 5-3 Location map for the South Fork of the Palouse River at Pullman (Anderson et al., 2008)..218 Figure 5-4 Cross sections for the South Fork of the Palouse River at Pullman (Anderson et al., 2008). 219 Figure 5-5 Hydrographs for WSU test well and Pullman well #8 in comparison to the discharge record for the South Fork of the Palouse River at Pullman...... 220 Figure 5-6 Hydrograph for the Cornelius well comparison to the discharge record for the South Fork of the Palouse River at Pullman...... 221 Figure 5-7 Locations of wells and cross sections in the vicinity of the City of Palouse (Bush and Garwood, 2005f)...... 222 Figure 5-8 Cross sections A-A’ and G-G’ in the vicinity of the City of Palouse (Bush and Garwood, 2005f)...... 223 Figure 5-9 2007-2008 hydrograph for the City of Palouse wells in comparison to the discharge record for the Palouse River at Potlatch...... 224 Figure 5-10 2008-2009 hydrograph for the City of Palouse wells in comparison to the discharge record for the Palouse River at Potlatch...... 225

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Figure 5-11 Winter water temperature data for City of Palouse wells (Gregory, personal communication, 2010)...... 226 Figure 5-12 Summer water temperature data for City of Palouse Wells (Gregory, personal communication, 2010)...... 227 Figure 5-13 Moscow area location map (modified from Bush, 2006a)...... 228 Figure 5-14 Geologic cross section through IDWR (Moscow) Well #4 (Bush, 2006a)...... 229 Figure 5-15 Cross section through the INEL well (Kopp, 1994)...... 230 Figure 5-16 2006-2009 hydrograph for the INEL-D and IDWR-3 wells in comparison to the discharge record for Paradise Creek at Moscow...... 231 Figure 5-17 Hydrograph for the INEL-D and IDWR-3 wells and discharge record for Paradise Creek at Moscow for the 2007-2008 water year...... 232 Figure 5-18 Location map for Klemgard Park along Union Flat Creek (Gregory, personal communication, 2010)...... 233 Figure 5-19 Hydrograph for the Klemgard Park well in comparison to the discharge record for the South Fork of the Palouse River at Pullman (Gregory, personal communication, 2010)...... 234 Figure 6-1 Barrier zone within the lower aquifer as postulated by Barker (1979)...... 255 Figure 6-2 Map showing the proposed study site for the investigation of the Pullman area hydrogeology...... 256 Figure 6-3 Depth to water data for WSU Knot Dairy Farm wells...... 257 Figure 6-4 Possible monitor well locations within the Wilber Creek and Union Flat Creek Valleys. ....258 Figure 6-5 Stream gain–loss characteristics (Sinclair and Kardouni, 2009)...... 259 Figure 6-6 Field measurement sites in the Pullman area for the WDOE stream gain-loss study (Sinclair and Kardouni, 2009)...... 260 Figure 6-7 Map showing depth to the top of the Grande Ronde Formation and the proposed surface-water / ground-water study area (After Robischon, 2010a)...... 261 Figure 6-8 Working boundary for the Palouse Ground Water Basin showing study site for the upper aquifer study (after PBAC, 2009c)...... 262 Figure 6-9 Generalized geologic map of the Palouse Basin showing the Kamiak Butte – Angel Butte gap study area (Bush and Garwood, 2005d)...... 263

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Palouse Ground Water Basin Framework Project FINAL report

List of Tables Table 3-1 Municipal and university well inventory (4 pages) ...... 160 Table 3-2 Surface-water discharge balances for the South Fork Palouse River and Paradise Creek stream corridor (from Sinclair et al., 2009)...... 164 Table 3-3 Surface-water discharge balances for the Palouse River (from Sinclair et al., 2009)...... 165 Table 3-4 List of recharge values reported in the literature (2 pages) ...... 166 Table 3-5 Barker (1979) water budget information for pre-development and 1975 conditions...... 168 Table 3-6 Barker (1979) predictive water budget information for 1976 pumping rate and two different rates of pumping increase...... 169 Table 3-7 Lum et al. (1990) summary of water budget for time-averaged simulation...... 170 Table 3-8 Lum et al. (1990) simulated average flow into selected rivers and measured stream discharges...... 171 Table 4-1 Historical water-level measurements from the US Geological Survey (5 pages)...... 195 Table 4-2 Wells in the program that were not able to be measured in 2010...... 200 Table 4-3 Well and water-level measurement data for wells measured in 2010 (2 pages)...... 201 Table 4-4 Rates of water-level decline (2 pages)...... 203 Table 5-1 Well inventory for surface-water/ground-water interaction task...... 236

Appendices Appendix A - Data quality assessment of reviewed documents technical memorandum Appendix B - Well logs Appendix C - Quality Assurance Project Plan (QAPP) Appendix D - Comments to drafts and response to comments

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Palouse Ground Water Basin Framework Project FINAL report

Acronyms and Abbreviations

ASR aquifer storage and recovery amsl above mean sea level bgs below ground surface CRBG Columbia River Basalt Group dpi dots per inch GIS geographical information system GRB Grande Ronde Basalt IDWR Idaho Department of Water Resources IWRRI Idaho Water Resources Research Institute m meter ma million years ago NA not applicable PBAC Palouse Basin Aquifer Committee pdf portable document format PMB (Pullman-Moscow Basin) QA quality assurance QA/QC quality assurance/quality control QC quality control RASA Regional Aquifer System Analysis RHS Ralston Hydrologic Services S&T Summary and Tracking South Fork South Fork of the Palouse River SQL Structured Query Language SR state route [road] TerraGraphics TerraGraphics Environmental Engineering, Inc. UI the USGS United States Geological Survey WDNR Washington State Department of Natural Resources WDOE Washington State Department of Ecology WSU Washington State University

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Executive Summary The Palouse Ground Water Basin includes the portion of the Palouse River Drainage Basin above the confluence of the North Fork and South Fork of the Palouse River that is underlain by basalt as defined by the Palouse Basin Aquifer Committee (PBAC) at the time of this project (see Figure 1.1). The Basin also includes a portion of the Union Flat Creek drainage. The Palouse Ground Water Basin is hereafter called the “Palouse Basin” or “Basin.” Two main aquifers exist in the Palouse Basin: the upper and lower aquifers. Drinking water for the municipalities and universities is mostly from the lower aquifer, where ground-water levels have been declining over the last 100 years. The Framework Project was developed to compile existing ground-water research, evaluate the status of knowledge, and provide recommendations for future work that will aid in a greater understanding of the aquifers for better ground-water management decisions. The Framework Project entails four primary tasks. These tasks include 1) a compilation task of assembling Palouse Basin geologic and hydrogeologic documents and creating a database, 2) a synthesis task of reviewing and synthesizing the documents, 3) a data-gap task of identifying areas of deficiency in the hydrogeologic literature, and 4) a conclusions and recommendations task. An additional task, Task 4.5, entails a preliminary data-gap investigation involving two projects: 1) surface-water / ground-water interaction and 2) mass water-level measurement study in the area west/southwest of Pullman. Compilation Task The Compilation task consisted of the following subtasks:  Searching for and collecting relevant documents, where “documents” refer to all forms of information (e.g., reports, videos, maps, etc.).  Creating digital versions of the documents.  Developing a Microsoft Access database to contain metadata information on the hydrogeology of the Palouse Ground Water Basin.  Conducting quality assurance/quality control (QA/QC) activities. All documents related to hydrogeological research conducted within the defined boundaries of the Palouse Basin that were acquired were reviewed and are included in the database. The database contains information on 339 reviewed documents, including geologic and geophysics studies, hydrogeologic studies, shallow sediment studies, and surface-water studies that are related to ground water. Thirty-six (36) documents with limited relation to the Palouse Basin have basic information included in the database but were not thoroughly reviewed because they were not directly relevant. Approximately nine studies conducted outside the Basin (i.e., the University of Idaho (UI) Troy research site) are included in the database because the work was deemed relevant to the Palouse Basin. Summary and Tracking (S&T) sheets were utilized to record pertinent information on each document. The S&T sheets were used internally to house the information that would be entered into the database and are not part of the product of Task 2. The following information, when available, is provided for each document:  Reviewer

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 Review date  Title  Author(s)  Year  Source  Type  Location  Scale  Subject  Data tracking  Data quality  Keywords  Well construction data  Comments  Source location  Ranking  Description – Brief description of the document, written by the reviewer  Author’s conclusions – Either taken verbatim or summarized  Author’s recommendations – Either taken verbatim or summarized Each document was ranked into one of the following five categories: o #1 Primary source documents – These are the most important documents related to the major topics of importance to the Palouse Basin (hydrogeology, geology, surface-water/ground-water interaction, geophysics and management). Examples include Barker (1979) and Lum et al. (1990). o #2 Secondary source documents – These documents include useful information related to the major topics of importance to the Palouse Basin. This category includes selected university theses, basic data and summary reports created by professionals, and large scale geologic studies. o #3 Analysis of source documents – This category includes articles and presentations based on work reported within primary or secondary documents. Examples include journal articles and/or Microsoft® Office PowerPoint presentations based on university thesis projects. o #4 Limited applicability documents – This category includes those papers and/or reports that provide information on a specific aspect of the Palouse Basin but do not add significantly to understanding the Basin hydrogeology. Examples include

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a number of the University of Idaho and Washington State University (WSU) theses that address specific topics in localized areas (e.g., a dissolved oxygen study in shallow wells). o NR – Not Reviewed – This category includes documents that are not directly related to the Palouse Basin. These documents were not thoroughly reviewed; only minimal information is provided in the database. A Microsoft® Office Access database was developed for containing the document information listed above, complete with tables, forms, queries, and reports. The database was designed to be continually updated as new documents are produced and recorded. Synthesis Task The purpose of the synthesis task was to synthesize or summarize the pertinent Palouse Basin hydrogeological documents. The synthesis chapter is divided into the following subsections:  Geologic Framework o Geologic nomenclature o Regional geologic characteristics o Palouse Basin geologic characteristics o Description of stratigraphic and structural features  Hydrogeologic Framework o Aquifer identification and temporal growth of knowledge o Characteristics of the lower aquifer o Characteristics of the upper aquifer o Ground-water flow systems  Water Balance o Surface-water gain/loss o Surface-sediment water balance o Upper-aquifer water balance o Lower-aquifer water balance o Ground-water age-dating analysis  Numerical Models o Barker (1979) model o Lum et al. (1990) model o Post Lum et al. (1990) analysis o Comparison of field data to numerical model predictions

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Preliminary Data Gap Investigation Task A preliminary data gap investigation task was added during the Framework Project to further investigate certain preliminary data gaps identified during the synthesis task. Two preliminary data gaps were identified and the associated projects conducted. These were: o A surface-water/ground-water interaction study conducted within the current boundary of the Palouse Basin. o A mass water-level measurement project conducted west-southwest of Pullman to investigate the theory of a ground-water barrier zone postulated by Barker (1979). Surface-Water / Ground-Water Interaction The purpose of the surface-water/ground-water investigation was to compare stream-flow records to hydrographs from selected wells to ascertain the degree of hydraulic connection between surface water and ground water at selected sites within the Palouse Basin. The analysis includes consideration of three stream segments in connection to two aquifers. The focus of this study is on periods of high flow within each of the target streams. The locations are as follows: o South Fork of the Palouse River in Pullman in relation to the lower aquifer, o Palouse River in Palouse in relation to the lower aquifer, o Paradise Creek in Moscow in relation to the upper aquifer, and o Union Flat Creek in relation to a well believed constructed in basalt of the Grande Ronde Formation. Hydrographs for wells completed in the lower aquifer are compared to the flow record for the South Fork of the Palouse River for two wells within Pullman (WSU test well and Pullman well #8) and one well near the river about six miles southeast of Pullman (Cornelius well). There is no discernible impact of high flow in the South Fork of the Palouse River on the water level in any of the three wells during the period of record examined. The flow record for the Palouse River is compared to hydrographs for the two City of Palouse wells completed in the lower aquifer (Palouse wells #1 and #3). Similarly, there is no discernible impact of high flow in the Palouse River on the water levels in either of the City of Palouse wells completed in the lower aquifer. Although temperature signatures within the wells correspond in part to temperature fluctuations in the river, this occurrence explained by the position of the data logger within the well. Given the hydrogeologic setting of the Moscow area, it is logical to evaluate the potential hydraulic connection of Paradise Creek with the upper aquifer. It has been shown that shallow wells located in the upper aquifer at the UI Groundwater Field Laboratory respond to water-level fluctuations in Paradise Creek. However, the hydrographs for two upper aquifer wells that are completed near the bottom of the aquifer (INEL-D and IDWR-3) do not show any response to high-flow events in Paradise Creek. The hydrograph for the Klemgard Park well, which is located close to Union Flat Creek and completed opposite a basalt flow in what is believed to be the Grande Ronde Formation, is compared with the flow record for the South Fork of the Palouse River in Pullman. This analysis is based on the assumption that precipitation events affect the creek and river similarly. There is

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no stream gauge on Union Flat Creek. The hydrograph does show a correlative response to a high-flow event, suggesting a hydraulic connection exists at that location. Mass Water-Level Measurements Barker (1979) conducted a mass water-level measurement project in an area west of Pullman, Washington in 1973 and 1974. He postulated that lower hydraulic conductivity in the lower aquifer in this area acted like a ground-water “barrier zone.” Ground-water levels were measured during June-August 2010 in wells with historical data in order to investigate this “barrier zone.” Thirty-seven (37) wells were targeted in this area. Twelve (12) of these wells were measured in 2010. The remaining wells could not be measured due to a number of factors including: the current well owner could not be located or would not give permission for the well to be measured; the selected well could not be identified in the field, had been destroyed, or had collapsed; and field conditions made it impossible to obtain a water- level measurement. Four of the 12 wells may be completed in the lower aquifer. One well has the same characteristics (geologic completion, water-level elevation, and rate of water-level decline) as the lower aquifer wells in Pullman. The remaining three wells had either higher ground-water elevations than expected or a lower rate of water level decline, or are completed shallower than expected. The different characteristics of these wells may be related to the “barrier zone” as postulated by Barker (1979). Data Gaps A large body of knowledge has been accumulated relative to the hydrogeology of the Palouse Ground Water Basin, particularly the Pullman-Moscow subarea. Although the 339 documents collected and reviewed provide a great deal of information, they do not necessarily provide the basis to respond to a number of important hydrogeologic questions, particularly those related to long-term water supply. The data gaps analysis included delineation of a prioritized list of data gaps and guidance relative to investigation programs needed to satisfy the high- and medium-priority information needs. Data gaps associated with surface water, including water sources for aquifer storage and recovery projects, are not addressed in this document. The data gaps listed in this report meet two criteria:  The data gap must be directly related to long-term utilization of ground water as a water supply with particular emphasis on the Pullman-Moscow subarea.  The data gap must be defined such that the investigational program has a reasonable chance of success. The data gaps are classified by priority as high, medium, and low as listed below.  High-priority data gaps: o The hydrogeology west of Pullman. o Surface-water/ground-water interaction northwest of Pullman. o Maximizing upper-aquifer pumping in the Pullman-Moscow subarea.

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 Medium-priority data gaps: o A ground-water monitoring program. o Lower-aquifer continuity in the Kamiak Butte to Angel Butte gap. o Hydraulic sub-basins within the Pullman-Moscow subarea. o Relationship between pumping and water-level decline. o Create a well-log databank.  Low-priority data gaps: o Ground-water conditions in the Colton, Uniontown, and Genesee areas. o Ground-water conditions in the Garfield area. o Ground-water conditions in the Colfax area. o Surface-water/ground-water interaction northeast of Colfax. The first two of the three high-priority data gap studies should be conducted before any of the other studies. All of these suggested studies involve drilling additional wells. The construction of new wells is an essential aspect of improving hydrogeologic knowledge of the Palouse Basin.

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Section 1.0 Introduction

The Palouse Ground Water Basin, hereafter called the “Palouse Basin” or “Basin,” is located in eastern Washington and northern Idaho. Figure 1-1 shows the current working boundary of the Basin. Note that the boundary is not coincident with the drainage basin of the Palouse River as it excludes some portions of the basin that are not underlain by basalt and includes a portion of the Union Flat Creek basin. Ground-water users within the Basin include the cities of Pullman, WA, Palouse, WA, Colfax, WA, and Moscow, ID; Washington State University (WSU); the University of Idaho (UI); and private well owners. The general geology consists of sediments overlying layers of basalt. The two basalt aquifers in the Basin are the upper aquifer and the lower aquifer. The lower aquifer supplies 64-81% of the water to Moscow, most of the water used by UI, and all of the water used by Pullman, Palouse, Colfax, and WSU. The upper aquifer supplies 19-36% of the water to Moscow and a portion of the water used by UI (Robischon, personal communication, 2010). Since the first area wells were drilled in the 1890s, water levels in the basalt aquifers have declined because of ground-water pumping. In the earliest report dated from 1897, Russell describes the construction of wells in Pullman and Moscow and suggests restricting the discharge from the flowing artesian wells. Since then, hundreds of geologic and hydrogeologic studies have been conducted in the Basin.

1.1 Purpose and Objectives

The overall purpose of the Palouse Ground Water Basin Framework Project is to compile, make available, and evaluate the current knowledge of the Palouse Basin and to identify data gaps and critical future projects. Objectives of the project as stated in the project proposal are to: “compile, review, and evaluate the completeness of information on the ground- water resources in the basin in anticipation of conducting a future full-scale site characterization project.” Specific objectives include conducting the following tasks. These are:  Task 1 – Project Management: Administrative preparation of the project.  Task 2 – Compilation: Compile all the geologic and hydrogeologic reports, maps, and cross sections. This includes searching, documenting, scanning, reviewing, summarizing, and creating a metadata database of these documents.  Task 3 – Synthesis: Synthesize the pertinent work that has been conducted in and about the Basin, and evaluate the quality of the documents.  Task 4 – Data Gaps: Develop data gaps based on knowledge gained in Task 3.  Task 4.5 – Preliminary Data Gap Investigation: Investigate and report on preliminary data gaps found during Tasks 2 and 3. This task was added to the scope of work during the project. The first preliminary data gap investigation was a mass water-level measurement project; the second was an investigation of the surface-water / ground-water connection in the Basin at specific locations.  Task 5 – Conclusions and Recommendations: Present a discussion, conclusions, and recommendations for future work.

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Draft reports for Tasks 2, 3, 4, 4.5, and 5 were submitted over the course of the project. Comments on the draft reports were received and incorporated into this final report. Appendix D includes a list of comments and a response to comments.

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Chapter 1 Figures

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Figure 1-1 Current boundary of the Palouse Ground Water Basin.

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Section 2.0 Task 2 – Compilation

Task 2 data compilation consisted of the following subtasks: 1) searching for and collecting relevant documents, 2) creating digital versions of the documents including scanning of oversize hard copies, 3) developing a Microsoft Office Access® database to contain metadata information on the hydrogeology of the Palouse Ground Water Basin, and 4) conducting quality assurance/quality control (QA/QC) activities. “Documents” refer to all forms of information (e.g., reports, videos, maps, etc.).

2.1 Collection

2.1.1 Documents Included TerraGraphics carried out an extensive search for existing documents related to hydrogeological research conducted within the basalt portion of the Palouse Basin. All relevant documents acquired were reviewed and are included in the database. The database contains information on 339 reviewed documents, including geologic and geophysics studies, hydrogeologic studies, shallow sediment studies, and surface water studies that are related to ground water. Thirty-six (36) of these documents have limited relation to the Palouse Basin and have basic information included in the database but were not thoroughly reviewed because they were not directly relevant. Approximately nine of the 339 studies conducted outside the Basin (i.e. the University of Idaho Troy research site) have details included in the Task 2 database because the work was deemed relevant to the Palouse Basin.

2.1.2 Documents Excluded Topics of information generally not included in the database consist of: 1) hydrogeologic studies conducted in the crystalline rock with the exception of surface water runoff, 2) less-related shallow sediment studies, 3) water quality studies, 4) surface water studies unrelated to ground water or water supply, and 5) studies conducted outside the Palouse Basin. The studies of crystalline rock areas such as Moscow Mountain were excluded because they have no direct bearing on ground water resources in the basalt and associated sediments. Shallow sediment studies such as soil surveys also were excluded because of a lack of relevance. Studies of surface water chemistry were uniformly excluded whereas studies of isotope ground water chemistry related to age dating were included. Surface-water flow studies were excluded except for those that pertained to flow gains and losses from ground water. Finally, studies had to have at a minimum a partial focus on the Palouse Basin to be included. Exceptions to this include geologic reports that pertain to the source areas of the basalt and reports resulting from studies of ground water in loess at the UI research site located near Troy, Idaho. In the latter case, the results of the loess hydrogeology studies are believed to be transferable to the Palouse Basin.

2.1.3 Search Locations Documents were collected from a variety of locations and individuals including:  C. Kent Keller  City of Moscow  City of Pullman

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 Dale Ralston  Geological Society of America  Idaho Department of Water Resources (IDWR)  Idaho Geological Survey  Idaho Water Resources Research Institute (IWRRI)  Latah County  Palouse Basin Aquifer Committee (PBAC) Library (format received sometimes distinguished only for this source) o CDs o Electronic format o Hard copy format  Paul McDaniel  United States Geological Survey (USGS)  University of Idaho (UI) Library o General Reference o Government Documents o Idaho Waters Digital Library o Interlibrary Loan o Special Collections  Washington State Department of Ecology (WDOE)  Washington State Department of Natural Resources (WDNR)  Washington State University (WSU) o Civil Engineering Department o Library – General Reference . WSU Library Palouse Digital Project o Library – Special Collections  Whitman County Requests and/or searches were also made to the following entities but no additional related documents were found:  City of Palouse  City of Colfax  UI Physical Plant

2.1.4 Related Documents Not Found In a very few instances, documents cited in a reviewed hydrogeologic document could not be located. Generally, this was because the citation was incomplete or the item in question was an unpublished historical document.

2.2 Compilation

2.2.1 Electronic Copies of Documents Electronic copies of all the documents listed in the database are provided as a deliverable. Filenames are included within a corresponding field of the database. A chronological list of documents is provided at the end of this report. Each document was collected in electronic

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Palouse Ground Water Basin Framework Project FINAL report format or scanned from hard copy. All black and white scans have a resolution of 300 dots per inch (dpi). Most documents are provided in portable document format (pdf), with the exception of videos, Microsoft® Office PowerPoint presentation slides, Microsoft® Office Excel spreadsheets, Microsoft® Office Access databases, and supporting document files (e.g., geographical information system (GIS) files, survey files, etc.). These are provided in the same format as TerraGraphics/Ralston Hydrologic Services received them to allow additional flexibility for the user. Plates downloaded from the USGS are also provided in djvu format, which has a better resolution than pdf. The file name nomenclature has first the year, followed by the author(s), and lastly either the beginning of the title or a short description of the document.

2.2.2 Collection of Information Summary and Tracking (S&T) sheets were developed in Microsoft® Office Word 2003 and utilized to record pertinent information on each document. The S&T sheets were used internally to house the information that would be entered into the database and are not part of the product of Task 2. The following information, when available, is provided for each document:  Reviewer – Either Dr. Nimmer, Dr. Ralston, or Mr. Lahiri conducted initial reviews of the documents and completed the S&T sheets. Dr. Nimmer and Dr. Ralston together reviewed all the S&T sheets for consistency prior to entry into the database.  Review date – Date of initial review.  Title – Official title of the document when provided or unofficial title if no title was provided.  Authors – Author(s) of the document.  Year – Year published or year completed if unpublished.  Source – Reference for the document.  Type o Abstract o Database o Personal o Thesis communication o Article o Dissertation o Poster o Video Correspondence Map Presentation o o o slides Cross section Meeting minutes Reference list o o o Data Ordinance Report o o o  Location – Location of study area.  Scale o Individual well scale – Reports that deal with the construction or testing of an individual well or a very localized site study, such as infiltration at a single site.

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o Local scale – Reports that include information on a small area, less than one square mile. Examples include the construction of the Idaho Department of Water Resources (IDWR) monitoring wells located north of the Palouse Empire Mall, and studies at the UI Groundwater Research Site or at the Whitman County Landfill site. o Intermediate scale – Reports that cover areas approximately between 1 and 10 square miles. Reports dealing with all of the wells for the City of Moscow or the City of Pullman are included in this category. o Sub-basin scale – Studies of large areas but less than approximately 75 percent of the Palouse Basin. An example would be a study of the Idaho portion of the Basin. o Basin scale – Studies that include more than 75 percent of the Palouse Basin. The Lum et al (1990) numerical model studies of the Basin would be an example. o Greater than basin scale – Reports or geologic maps and studies of the Columbia Basin that include the Palouse Basin in both Idaho and Washington. o NA (not applicable) – Studies conducted outside the Basin but important to the analysis of the hydrogeology of the Basin (e.g., at the UI Troy research site).  Subject o Aquifer boundary – Studies that evaluate the boundaries of the aquifers. o Aquifer storage and recovery (ASR) projects – Studies of ASR and artificial recharge projects. o Borehole video log – Borehole video logs of wells within the Basin. o Geologic mapping – Surface geologic maps on a wide range of scales and detail. o Geologic cross sections – Cross sections that are diagrammatic and those that are based on analysis of individual wells. o Geologic stratigraphic interpretation – Analysis of the stratigraphic section in an individual well but also general stratigraphic analysis, as well as all other geologic studies (geophysics, geochemical, etc.). o GIS files – Reports or data that include GIS files. o Ground-water contour mapping – Maps of ground water contours. o Ground-water management –Studies of various ground water management alternatives such as declaration of critical ground water areas. o Ground-water pumping analysis – Studies of pumping by individual entities ranging up to Basin-wide analysis. o Ground-water supply – Ground water related studies that do not fit into other subject categories. o Hydrogeochemistry – Studies on ground water geochemistry.

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o Individual well hydraulic analysis – Aquifer tests conducted on individual wells would be included under this subject. o Multiple well hydraulic analysis – Aquifer tests and tracer tests in which multiple wells are used. o Numerical modeling – Reports on numerical models of Basin hydrogeology. o Recharge analysis – Studies ranging from soil-water balance such as work at the UI and WSU research sites to Basin water level interpretations. o Reference list – Reports listing documents pertaining to the hydrogeology and geology of the Palouse Basin. o Surface-water/ground-water interaction – Studies of stream gain and loss as related to ground water. Water balance and water quantity reports are also included here. o Surface-water supply – Surface water studies related to water supply. o Water balance – Studies of a water balance (water inputs and outputs). o Water dating – Isotope studies used to determine the ages of ground water. o Water-right analysis – Water rights for entities or individuals within the Basin. o Water-temperature analysis – Studies on ground water or surface water temperature. o Water use – Studies on the use of water.  Data tracking o Original data o Non-original data  Data quality o Collected by professionals – Field data collected by geologic and hydrogeologic professionals. There is an underlying assumption that a stated or unstated QA/QC program was followed. o Collected by students – Field data collected by students. The field data collected by students are likely of considerable value; however, they are not as reliable as those collected by professionals.  Keywords – Selected pertinent words that describe the document. A lengthy list of keywords can be found in the database under the object “Tables” then “key_words.”  Well-construction data – Noted if well construction data are provided.  Comments – Provided when a specific comment is warranted (e.g., if a map in a report is missing and not found).  Source location – Location where the document was found.  Ranking

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o #1 Primary source documents – These are the most important documents related to the major topics of importance to the Palouse Basin (hydrogeology, geology, surface-water/ground-water interaction, geophysics, and management). Examples include Barker (1979) and Lum et al. (1990).

o #2 Secondary source documents – These documents include useful information related to the major topics of importance to the Palouse Basin. This category includes selected university theses, basic data and summary reports created by professionals, and large-scale geologic studies.

o #3 Analysis of source documents – This category includes articles and presentations based on work reported within primary or secondary documents. Examples include journal articles and/or Microsoft Office PowerPoint presentations based on university thesis projects.

o #4 Limited applicability documents – This category includes those papers and/or reports that provide information on a specific aspect of the Palouse Basin but do not add significantly to understanding the Basin hydrogeology. Examples include a number of the UI and WSU theses that address specific topics in localized areas (e.g., a dissolved oxygen study in shallow wells).

o NR – Not Reviewed – This category includes documents that are not directly related to the Palouse Basin. These documents were not thoroughly reviewed; only minimal information is provided in the database.  Description – Brief description of the document written by the reviewer.  Author’s conclusions – Either taken verbatim or summarized.  Author’s recommendations – Either taken verbatim or summarized.

2.3 Database Organization

The database was created in Microsoft® Office Access. When the file is initially opened a “Menu” window is at the forefront. Within the Menu there are six buttons to help navigate through the database in a simplified manner. The first is “Enter Data”; this opens a form in which one can enter new data. The “Search” button allows the user to search for a document and display information for a particular document. There are four canned report buttons. These include: “Bibliography by year,” “Bibliography by author,” “View all document data,” and “Save all data to Word.” A more in-depth description of the following objects can found on the left-hand side when the database is opened: TABLES, FORMS, QUERIES, and REPORTS. Some of the items within these objects were used to develop the database and others are to be used by the database user. The nomenclature used henceforth is , for example, TABLES – documents. The current names of tables, forms and queries must not be changed as doing so would break the

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Palouse Ground Water Basin Framework Project FINAL report connectivity of the database functions. The following is a brief description of all the fields (or names) found in each type of object as well as useful information for the database.

2.3.1 Database - Tables Within the Tables object (Figure 2-1), there are a number of tables that support the comprehensive table, called TABLES – documents. TABLES – documents includes all of the information from the S&T sheets except for subjects and keywords. Subjects and keywords are not included in that Table because there can be more than one subject or keyword for a single document. Consequently, these items are found in separate tables called TABLES - documents_subjects and TABLES - documents_key_words, respectively. The remaining tables are used as items for the dropdown menus within the data entry form (Forms – documents, described below). Figure 2-2 shows the relationships of how the tables are connected, as compiled by Access. Fields found in TABLES – documents correspond to the “documents” box in Figure 2-2. The “oo” symbol next to a field indicates it has an additional table (see Figure 2-1). These fields require additional tables because they occur as drop down menus in the data entry form. For example, only one scale is allowed per document, but there is a list of the scales to choose from. The information in the boxes reflects the information shown in the drop down menu. The two boxes immediately to the right of the “documents” box represent fields that are not explicitly included but are linked as additional tables, again because there can be more than one subject or keyword for a single document. For example, there is a list of the subjects to choose from and several subjects are allowed per document.

2.3.2 Database - Forms Within the Forms object (Figure 2-3), there are five Forms. The data have been entered from the S&T sheets into the FORMS - documents. This is the Document Entry Form. In this Form, some of the fields are free text and others have drop down menus. There is also a check box to be selected if the document provides well construction data. All of the data on a single document can be found here. There are two other Forms that support the FORMS - documents. These are FORMS - documents_subjects and FORMS - documents_key_words, which are needed because a single document may require multiple subjects and keywords. The FORMS – printable_input_form allows the user to print all the fields for an individual record. Microsoft Access has a limitation in that it cannot have a continuous form with sub-forms. This means that displaying all the data for a record and printing more than one record at a time can be very difficult to implement without additional Visual Basic programming and associated expenses. The Form titled FORMS – Search_PBAC allows the user to create search criteria for a single item or multiple items. The output is in either: 1) table format (printable check box is not checked) which displays the year, author(s), and title, or 2) printable format (check the printable check box) which displays the search criteria, year, author(s), title, source, description, author’s conclusions, and author’s recommendations.

2.3.3 Database - Queries Within the Queries object (Figure 2-4), two queries have been generated. These are QUERIES – qrySearch and QUERIES – Document_query. This object is basically a container for dynamic

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Structured Query Language (SQL). The SQL used by the query will dynamically change based on what was selected in the FORMS-Search_PBAC.

2.3.4 Database - Reports Within the Reports object (Figure 2-5), two reports have been generated to provide specific information about the documents. The first Report, REPORT - Framework Project Bibliography by Year, lists the year, author(s), and title. The second Report, REPORT - Framework Project Bibliography by Author, lists the author(s), year, and title, and is included as a deliverable for this task (Task 2). The third report, REPORT - rptSearch, displays the results of the latest search from the FORMS-Search_PBAC.

2.3.5 Database User The database user will most likely be interested in TABLES – documents, FORMS – documents, FORMS – printable_input_form, FORMS – search_PBAC, and REPORTS - Framework Project Bibliography by Author (or year).

2.4 Quality Assurance/Quality Control

To ensure a quality product, the project included multiple QC points throughout the process. These include:  Close contact/communication between team members continued throughout the project.  Dr. Nimmer and Dr. Ralston conducted a secondary review of each S&T sheet to ensure consistency of document reviews prior to entry into the database.  After staff entered all of the data into the database, the QA/QC team reviewed the first ten entries in the database and then reviewed every fifth entry for accuracy and completeness by comparing with the original document and the S&T sheet.  Additional QA/QC measures were instituted to ensure a quality product.

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Chapter 2 Figures

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Figure 2-1 Print screen of the Tables object within the database.

Figure 2-2 Table relationships as depicted by Microsoft Access.

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Figure 2-3 Print screen of the Forms object within the database.

Figure 2-4 Print screen of the Queries object within the database.

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Figure 2-5 Print screen of the Reports object within the database.

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Section 3.0 Task 3 – Synthesis

3.1 Introduction

The purpose of this chapter of the report is to present a synthesis of the pertinent literature and merge the geologic, hydrogeologic, and water balance knowledge of the Basin. All of the documents were reviewed but only the reports that provide a specific contribution are referenced in this report. The objective of this chapter is to summarize the knowledge of the Basin in the following general areas:  Geology  Hydrogeology  Water balance  Numerical models A reference list from the database is provided in Section 8.0 at the end of this report. An assessment of the data quality of the documents reviewed can be found in Appendix A. Note text within parentheses is part of the quotation; text within brackets is added by the authors of this report.

3.2 Geologic Framework

3.2.1 Introduction Much of the geologic information available for the Palouse Basin stems from work conducted or directed by Dr. John Bush, Professor Emeritus of Geology at UI. Dr. Bush completed a number of the major geologic publications in collaboration with Dean Garwood, presently employed by the Idaho Geological Survey. Dean Garwood is an excellent source for information on the local geology. Regional geologic maps of the Columbia Basin are available from the USGS. Dr. Steve Reidel of the Pacific Northwest Regional Laboratory in Richland, WA is an important information source for the geology of the Columbia Basin. The Palouse Basin, located along the eastern margin of the Columbia River basin, is underlain dominantly by basalt (Figure 3-1). Scientists delineate the eastern boundaries of the Palouse Basin based upon the contact of the basalt and associated sediment with the older metamorphic and intrusive igneous rock. Islands of basement rock (metamorphic and intrusive igneous) in the basalt are present west of a line connecting Pullman to Palouse. A basement rock ridge extends to the west immediately north of the town of Johnson and forms the southern boundary to the Basin in the immediate Pullman-Moscow area. The southwestern, western, and northwestern boundaries of the Palouse Basin are not defined based on geologic contacts. Most of the geologic and hydrogeologic information available for the Basin has a focus on the Pullman-Moscow area. A lesser amount of information is available for the Palouse and Colfax areas. Bush (2005d) divided the Palouse Basin into the following sub-regions for his summary paper on area geology: Moscow, Pullman, Uniontown, Colfax, Palouse, and Viola. For the purposes of this report, the Palouse Basin is divided into three subareas: Pullman-Moscow,

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Northern, and Western. The approximate boundaries of these three subareas are shown on Figure 3-1.

3.2.2 Geologic Nomenclature The growth of knowledge of the Columbia River Basalt Group resulted in a changing nomenclature relative to specific basalt units. The following description is taken from Reidel (1983, page 519).  Waters (1961) divided the Columbia River basalt into the Yakima Basalt and the Picture Gorge basalt based on differences in chemical composition, petrography, and flow characteristics.  Wright et al. (1973) divided the Yakima Basalt into upper, middle, and lower formations and demonstrated that these formations contain flows or groups of flows with distinct chemical compositions.  Swanson et al. (1979) renamed the upper, middle, and lower Yakima Basalts as the Saddle Mountains, Wanapum, and Grande Ronde Basalts, respectively.  Swanson and Wright (1976) showed that the Grande Ronde Basalt could be subdivided in the field using four paleomagnetic intervals: R1, N1, R2, and N2. The geologic references for the Palouse Basin reflect the changing nomenclature, depending on the time the work was done. Geologic discussions within this text are based on the formation names developed by Swanson et al. (1979): Saddle Mountains, Wanapum, and Grande Ronde Basalts.

3.2.3 Regional Geologic Characteristics Drost et al. (1990, page 1) provide a description of the regional geologic setting of the Columbia Plateau. Figure 3-2 shows the lateral extent of the Columbia River Basalt Group. “The Columbia Plateau of eastern Washington, north central and northeastern Oregon and western north Idaho covers more than 70,000 square miles and is underlain mostly by basalt of the Columbia River Basalt Group. The Plateau is a large structural basin whose deepest part lies near Pasco, Washington where the total thickness of basalt may exceed 14,000 feet… “Dominant geologic structures in the Yakima Fold Belt in the western portion of the Plateau are long, narrow ridges that are sharply folded and faulted, with intervening large synclinal basins. Basalt units in the Palouse subprovince are inclined to the southwest, but are gently warped in places by northwest and southwest trending low amplitude folds. The Blue Mountains province of the southeastern portion of the Plateau is a broad, deeply dissected, uplifted region and crossed by northeast trending folds and by north to northwest trending normal faults and lineaments.” Mangen and Wright (1984, page 1) provide the following description of the Columbia River Basalt Group. “The flood basalts of the Columbia River Basalt Group of Miocene age cover more than about 2 x 105 km2 in Washington, Oregon and Idaho. The most voluminous member of the Columbia River Basalt Group, the Grande Ronde Basalt (GRB), erupted for about 2

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m.y. [million years] from north-northwest fissure systems concentrated in SE [southeast] Washington. Regional correlation of GRB flows is based on chemical and magnetic data… “The GRB chemical types define specific stratigraphic units which range from 30 to 150 m [meters] thick and can be traced laterally over great distances… “The total thickness of the GRB flows is greatest in the center of the basin, intermediate in the western Plateau and least near the fissure systems. This indicates the presence of a WNW [west-northwest] dipping paleoslope and a shallow central basin during GRB time.” Swanson’s (1987, page 455) description of jointing characteristics of the Grande Ronde Basalt provides insight relative to the flow characteristics of this unit where the Palouse Basin is located along the eastern margin of the Columbia Plateau. “Reconnaissance mapping of most of the area covered by Grande Ronde Basalt revealed geographic variation in jointing style interpreted to reflect the presence or absence of water ponded on the lava flows as they cooled. The flows lapped against highland along much of the parameter of the province. Each flow buried the drainage system formed on the next older flow. Runoff from the highlands spread over the hot lava, in places as far as 40 km into the province… Invasive basalt flows are also common along the marginal [sp] of the province where clastic sediments accumulated.”

3.2.4 Palouse Basin Geologic Characteristics The geologic characteristics of the Palouse Basin are discussed relative to the three subareas that are shown on Figure 3-1. The Pullman-Moscow subarea includes the two cities plus the area underlain by basalt within the boundaries formed by crystalline rock outcrops. Boundaries are drawn across the gaps between Kamiak Butte and Angel Butte on the north and between Smoot Hill and Kamiak Butte on the northwest. The southwestern boundary is shown approximately midway between Pullman and Union Flat Creek. The Northern subarea includes the city of Palouse and the area underlain by basalt within the boundaries formed by crystalline rock outcrops. The Western subarea comprises all of the area included in the presumed boundary of the Palouse Basin west of the Pullman-Moscow and Northern subareas. The Western subarea includes the cities of Colfax and Garfield. Bush (2005d) divides the Palouse Basin into six sub-regions: Pullman, Moscow, Viola, Palouse, Colfax, and Uniontown. For this report, the Pullman, Moscow, and Viola sub-basins are included in the Pullman-Moscow subarea and the Colfax and Uniontown sub-basins are included in the Western subarea. The Northern subarea, as used in this report, includes the Palouse sub- basin of Bush (2005d).

3.2.4.1 Pullman-Moscow Subarea Controls for basalt emplacement along the eastern margin of the Columbia Plateau are described by Bush and Ralston (1997, page 1). The focus of this discussion is on the Pullman-Moscow portion of the Palouse Basin but the general information applies to all three subareas. A general stratigraphic section for the Palouse Basin is presented in Figure 3-3.

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“The geological setting of the aquifers within the Columbia River Basalt Group is distinctively different along the eastern margin than in the center of the basin… The key geologic factors controlling the basalt aquifers are as follows: 1) pre-basalt basement topography, 2) relation between marginal sediments and basalt units, 3) thinning and post-emplacement deformation of basalt units over subsurface basement highs, 4) onlap and offlap of Wanapum and Grande Ronde Formations near the basement contacts, and 5) character of the contact zone between the Priest Rapids Member of the Wanapum Formation and the Grande Ronde formation. “Basement rock highs, both those exposed and those covered by one or more basalt flows, form the boundaries of the Pullman-Moscow ground-water system… The lateral continuity of the upper and lower aquifers (Wanapum and Grande Ronde Formations) may be quite different depending on the relief of the pre-basalt topography. “Subsurface bedrock highs occur around the margins of the plateau and are very important in controlling aquifer continuity and ground water flow. A bedrock high may form the western ‘boundary’ of the Pullman-Moscow aquifer as represented in past ground water models… “Both onlap and offlap relations exist between the Grande Ronde and Wanapum Formations as the flows approach the edge of the plateau. Direct recharge to the Grande Ronde Formation is more likely in the offlap areas. In onlap areas, the thickness and hydraulic properties of the interbeds and/or saprolite zones play a role in regional ground water flow patterns.” Bush (1996) provides additional insight relative to the geologic framework of the Palouse Basin area with an emphasis on the Pullman-Moscow area. “At approximately 17 ma [million years ago] the first of the basalt flows, which belong to [the Imnaha Formation of] the Columbia River Basalt Group, were emplaced into the basin from the west. Early flows did not cover the entire basin but they disrupted erosional patterns and caused deposition of clastic sediments in the eastern end of the basin beneath what is now Moscow… Similar to the earliest flows, basalts of the Grande Ronde Formation (17 ma) also entered the basin from the west, most of which did not reach Moscow, while others extended as far as the present day eastern city limits. These flows are part of the same units that cover much of the present day Columbia Plateau and comprise over 80% of the volume of the Columbia River Basalt Group. In Moscow, these flows caused rapid sedimentation in environments that ranged from low energy lakes to high energy fluvial environments… Although the precise distribution of individual environments is not known, coarse deposition dominated near basement highs and fine deposition dominated to the west… Westward the sediments of Moscow thin rapidly towards the Washington-Idaho boundary and the Grande Ronde aquifer in Pullman consists primarily of basalt units (page 3). “At approximately 15 ma, the entire Plateau including Moscow was covered by a group of flows belonging to the Priest Rapids Member … of the Wanapum Formation. In Moscow, this flow or flows went over a thick sediment sequence (Vantage Member of Latah Formation) that now separates the Priest Rapids from the earlier Grande Ronde flows and sediments of Moscow. Along the very eastern end of the basin the Priest Rapids flowed onto basement rock highs, but in places there is vertical continuity

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between early and late sediments. Emplacement of the Priest Rapids flows again caused deposition of sediments from nearby weathered basement rocks. These sediments, referred to as the sediments of Bovill, form a westward thinning wedge over much of Moscow between the loess and the underlying basalt flow or flows, and in places lie directly on weathered crystalline rocks…(page 3) “The Vantage Member is a clay-rich interbed over much of Moscow, which acts in places as an aquitard and causes separation of the lower Grande Ronde and upper Wanapum aquifers over a part of the Moscow-Pullman basin. On the ‘very’ eastern edge of the basin, it is coarser and vertical connection in places from the surface to the Vantage and on down to the lower units of the sediments of Moscow is likely. Westward towards Pullman the Vantage interbed thins to a few feet in thickness and more exchange between the two aquifers is expected (page 4).” Additional clarification of the geologic framework is presented in Bush et al. (2001b, page 1). “Regional mapping in parts of the Clearwater embayment south and southwest of Moscow showed that the basalts are folded more than previously believed. Plateau areas of the CRBG [Columbia River Basalt Group] in Idaho north of the Clearwater River and in Washington north of the Snake River contain numerous low amplitude, long wavelength folds characterized by narrow asymmetrical anticlines separated by wide, nearly horizontal synclinal troughs. Utilizing detailed mapping in specific areas, well water data, and drainage analysis it can be demonstrated that similar folds exist west of Pullman… These folds trend and plunge to the northwest within a gentle northwest dipping thick block of basalt west and southwest of Pullman. The folds, in particular the narrow asymmetrical anticlinal parts, are potential geologic barriers to southwest ground- water flow between Pullman and the Snake River. In the plateau area west of Pullman, major drainages are to the northwest, the basalt flows dip to the northwest, stratigraphic horizons dip to the northwest, and feeder dikes occur that strike to the north-northwest. All of these same features are potential barriers to southwest flow towards the Snake River and it is concluded that most ground-water flow west of Pullman should be to the northwest. “Subsurface stratigraphic correlations using lithologic logs and basalt geochemistry in the Pullman area show that flow by flow correlation between wells is not as consistent as expected. Rapid changes in both interbed and flow thicknesses are common and geochemical basalt sequences thicken and thin within short distances between wells. These kinds of changes are common near prebasalt highs. Similar changes are also common where deformation was occurring during emplacement of the basalts …”

3.2.4.2 Northern Subarea The following description of the Northern (Palouse) subarea is taken from Bush (2005d, pages 42-43). “The ‘Palouse’ sub-basin is a semi-circular east-west shaped area that extends from Route 95 in Latah County, Idaho to its western boundary with the Colfax sub-basin [Western subarea] in Washington… Much of the sub-basin is defined by contacts of the CRBG [Columbia River Basalt Group] with older rocks. There are two gaps where the basalt extends across the older rocks. One of these gaps is to the south of the city of

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Palouse between Kamiak and Angel buttes. The second gap is in the northwest corner of the sub-basin where the Palouse River flows on basalt between older rocks on the north and south… “Outcrops of basalt in this sub-basin all belong to the Priest Rapids Member of the Wanapum… The geology appears to be simple, but the stream patterns suggest subsurface structural control… The western edge of the ‘Palouse’ … sub-basin is defined by the high in the upper Grande Ronde surface that borders the Colfax sub-basin between the communities of Palouse and Elberton.”

3.2.4.3 Western Subarea The Colfax and Uniontown sub-basins of Bush (2005d) are included in the Western subarea. Bush (2005d, page 40) describes the Colfax portion of the Western subarea as follows. “The Priest Rapids and Roza Members of the Wanapum Basalt and flows of the upper Grande Ronde are exposed along the canyon walls of the Palouse River… Interbeds of the Latah Formation crop out along canyon walls and are noted in most well logs, but rarely exceed 20 feet in thickness and generally consist primarily of clay… “The Colfax sub-basin is structurally simple in comparison to the other sub-basins. However, there are some features that suggest structural control could be important to ground-water flow. The Palouse River makes a sharp ninety degree turn from southwest to northwest at Colfax, which is opposite from the sudden turn to the southwest at Elberton.” The Uniontown portion of the Western subarea is described by Bush (2005d, page 37) as follows. “The combination of northwest trending structures and a different sequence of CRBG units separate this sub-basin geologically from all the other areas. The sub-basin contains several Saddle Mountains flows that overlie the Roza and Priest Rapids flows of the Wanapum. The Roza pinches out from west to east just south of Colton and in the eastern part of the sub-basin the Wanapum consists of only the Priest Rapids Member.”

3.2.5 Description of Stratigraphic and Structural Features The geologic framework of the Palouse Basin has been depicted in a number of plan maps and cross sections. The plan maps include the altitude of the top of the crystalline basement rocks, the altitude of the top of the Grande Ronde Formation, the altitude of the top of the Wanapum Formation, the depth to the top of the Grande Ronde Formation, and the location of structural features. Geologic cross sections include a generalized east-west section and more local cross sections in a number of orientations. The following portions of the report present and describe the plan-view maps and geologic cross sections.

3.2.5.1 Crystalline Basement Rocks There are only a few wells that penetrate through the basalt and intercept the underlying basement rocks. Thus, most of the understanding of the configuration of the crystalline basement rocks has been gained from surface geophysical studies. Brief summaries of the major geophysical studies are provided below.

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 A number of reports dealing with geophysical investigations of the Moscow portion of the Pullman-Moscow subarea were prepared in the 1960s by Crosby and Cavin of WSU. Cavin and Crosby (1966) provide the results of that effort in a map of the top of the crystalline rock underlying Moscow. The map shows a westerly system of ridges and deep valleys with the deepest part of the ancestral basin located north of the center of the city.  Jackson (1975) with the USGS reported on a surface resistivity study of the Pullman- Moscow area. The one-page abstract for this study provides the following information. “The pre-Tertiary basement complex increases in depth from about 425 meters (about 1,400 feet) at Moscow to at least 930 meters (about 3,000 feet) about 3 km east of Pullman. Structural contours, based on well control and sounding interpretations, define a depression on the basement surface centered about 2 km northwest [likely northeast and not northwest] of Pullman. The depression is closed to the west by a subsurface ridge on the basement about 5 km west of Pullman. This ridge may extend between outcrops of basement rocks at Albion, Washington, on the north and Chambers, Washington, on the south.”  Klein et al. (1987), also with the USGS, conducted a magnetotelluric survey of the Pullman-Moscow portion of the Palouse Basin in support of the Lum et al. (1990) numerical model study. Figure 3-4 shows the results of the magnetotelluric study in terms of the elevation of the crystalline basement rock (presented in Lum et al., 1990, Figure 7). The map shows that the basement rocks are as much as 1,000 ft higher in elevation immediately west of Pullman than slightly east of Pullman. The deepest portion of the ancestral basin is depicted to be east of Pullman with an elevation of less than sea level. The results the Klein et al. (1987) magnetotelluric survey are similar to the results of the Jackson (1975) resistivity survey in the Pullman area.  The Klein et al. (1987) study also shows that the elevation of the top of the crystalline basement rocks is less than 1,000 feet in the gap between Kamiak Butte and Angel Butte (Figure 3-4). The Klein et al. report (1987) would support the hypothesis that the upper portion of the Grande Ronde Basalt is continuous through the gap. The elevation of the top of the crystalline rocks is shown as higher than 2,000 feet in the gap between Kamiak Butte and Smoot Hill.  As his M.S. thesis project at UI, Holom (2006) conducted a gravity survey across the bedrock gap between Kamiak Butte and Angel Butte in the area south of Palouse. He concluded that basalt of the Wanapum Formation is continuous through the gap but that basalt of the Grande Ronde Formation is not continuous through the gap. Scaled from geophysical line #1 of Holom (2006), the minimum elevation of the top of the crystalline basement rocks is about 2,100 feet. Line #1 is a west-east line extending from the far northeast corner of Kamiak Butte (east of SR 27) to an area just north of Angel Butte up to Ringo Butte. Holom’s prediction of the elevation of the top of the crystalline rocks in the gap between Kamiak Butte and Angel Butte is considerably higher than that predicted by the Klein et al. (1987) survey.  WSU well #7 was constructed to a depth of 1,000 feet as a production well and then deepened as a test well in 1988 in an attempt to ascertain the accuracy of the geophysical

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predictions of the depth to basement rocks in the Pullman area (Wyatt-Jaykim and Ralston, 1987). Drilling was terminated at a depth of 2,224 feet without encountering crystalline basement rock. Based on the data from WSU well #7, the elevation of the top of the crystalline rock is lower under this portion of the campus than was predicted by Klein et al. (1987).

3.2.5.2 Imnaha Formation The Imnaha Formation underlies the Grande Ronde Formation over a large part of the Columbia Plateau (Figure 3-3). Rock chemistry data from the lower portion of WSU well #7 confirm that the lowermost basalt in the Pullman area is part of the Imnaha Formation (Bush, 2005d). According to Conray and Wolff (2010), the top of the Imnaha Formation is at an elevation of about 550 feet in the Pullman area. The Imnaha Formation is thought to be present only in the western portion of the Palouse Basin. The nearest area where the Imnaha Formation is used as a water supply source is the city of Kendrick, Idaho.

3.2.5.3 Grande Ronde Formation Mangan et al. (1986, page 1300) provides the following description regarding identification of specific units of the Grande Ronde Formation. Unit identification is based on two different approaches. A field instrument can be used to determine the magnetic signature of the basalt at outcrop sites. The magnetic orientation is shown as “N” for normal (North Pole) and “R” for reversed (South Pole), representing the conditions of the earth when the basalt was erupted. The second identification approach involves determining trace element concentrations in the rock. “Four magnetostratigraphic units are recognized in the Grande Ronde Basalt. From youngest to oldest, these units are designated N2, R2, N1, and R1. These units consist of numerous flows and range in thickness from 240 to 370 m [meters]. Regional mapping of the magnetostratigraphic units provides the broad stratigraphic framework for the formation… “The regional extent of specific flows within the magnetostratigraphic units of the Grande Ronde Basalt is not easily determined in the field, as nearly all flows are aphyric and fine grained with no distinctive field or petrographic characteristics… The work of Reidel … has shown that major- and trace-element chemistry of flows combined with relative position within magnetostratigraphic units can be used to correlate flows locally in the Grande Ronde Basalt…” Bush (2005b) presents a series of diagrammatic maps that show the emplacement of the various paleomagnetic members of the Grande Ronde Formation in the Pullman-Moscow area. Figures 3-5, 3-6, 3-7, and 3-8 show the extent of the R1, N1, R2, and N2 basalt flows, respectively, as projected by Bush (2005b). For comparison, Figures 3-9 and 3-10 show the extent of the Roza and Priest Rapids members of the Wanapum Formation. An east-west regional cross section, constructed by Bush (2005b), shows the relationship of the Imnaha Formation, the Grande Ronde Formation, the Wanapum Formation and the sedimentary units (Figures 3-11a and 3-11b). The panel diagram (Figure 3-12) prepared by Bush and Garwood (2005h) shows the various geologic units over the extent of the Palouse Basin. The Grande Ronde Formation in the Pullman-Moscow area includes a number of individual basalt flows. A lithologic log for IDWR well #4 is given below to illustrate the stratigraphic

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Palouse Ground Water Basin Framework Project FINAL report sequence for the Moscow area. This well is located about a mile north of the Palouse Mall. Figure 3-13 shows a geologic cross section constructed by Bush (2006a) through the IDWR well #4. The cross section shows that a large percentage of the subsurface consists of sediment of the Latah Formation. IDWR well #4 (Bush, 2006a) 0 to 2 feet top soil 2 to 50 feet Latah Formation: dominantly clay 50 to 276 feet Wanapum Basalt; Priest Rapids Member 276 to 499 feet Latah Formation: clay and sand layers

499 to 585 feet Grande Ronde Basalt: N2 member 585 to 720 feet Latah Formation: clay and sand layers

720 to 735 feet Grande Ronde Basalt: R2 member The geologic log for Pullman well #7 provides similar information for the Pullman area. Bush et al. (2001a, page 3) identified 10 to 11 basalt flow or flows units within the Grande Ronde Formation in Pullman well #7 along with two thin (15 feet and 28 feet) sediment units. They concluded that the upper portion of the basalt sequence likely belongs to the N2 member and the lower portion part of the sequence belongs to the R2 member of the Grande Ronde Formation. The geologic section constructed through Pullman well #7 (Figure 3-14) shows that sediments of the Latah Formation make up only a small percentage of the geologic section. Pullman well #7 (Bush et al., 2001a) 0 to 15 feet Sediment including soil, rubble and alluvium 15 to 47 feet Wanapum Basalt; Priest Rapids Member 47 to 87 feet Latah Formation: Vantage Member 87 to 720 feet Grande Ronde Formation: basalt and sediment Conrey and Wolff (2010) present a detailed stratigraphic cross section of the Grande Ronde Formation in the Pullman area (Figures 3-15a and 3-15b). Their work is based on recent X-Ray Fluorescence analysis of pellets that were created in the 1970s shortly after many of the area production wells were drilled. The Conrey and Wolff (2010) geologic cross section illustrates the complexity of the subsurface in the immediate Pullman area (Figure 3-15b). They postulate the presence of a northwest trending fault under the WSU campus to explain the offset of units between WSU wells #6 and #7. Bush and Garwood (2005f) prepared several cross sections that illustrate subsurface geology of the Northern and Western subareas. Figure 3-16 shows the locations of the sections. Cross sections A-A’ and G-G’ are near Palouse (Figure 3-17) and show a considerable thickness of sediment overlying and underlying the Grande Ronde Formation. Only the N2 member of the Grande Ronde Formation is shown to have entered the Palouse area. Section F-F’ is oriented southeast to northwest and extends through Elberton (Figure 3-18). The thickness of Grande Ronde Basalt is considerably greater near Elberton than in the Palouse area and both the N2 and the R2 members are shown in this area. Section E-E’, oriented southwest – northeast through

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Colfax, shows that the upper two members of Grande Ronde Formation are at least 1,000 feet thick (Figure 3-18). The top of the Grande Ronde Basalt is exposed along the lower portion of the river valley. Leek (2006) prepared a cross section that approximately follows the South Fork of the Palouse River from Pullman to Colfax. Figure 3-19 shows that the wells completed in the Grande Ronde aquifer in the Colfax area have much lower ground-water levels than wells completed in the same aquifer in the Pullman area. A number of authors have prepared maps of the top of the Grande Ronde Formation in the Palouse Basin. The Bush and Garwood (2005j) map probably is the most valid since it was constructed coupled with creation of plan-view bedrock geologic maps of the various quadrangles that make up the Palouse Basin. The map, presented on Figure 3-20, is based on evaluation of well driller logs from wells in the area plus mapped contacts. The highest elevation of the top of the Grande Ronde Formation shown on the map (2,400 feet) is at a location approximately midway between Moscow and Pullman. The elevation of the top of the formation decreases to the east toward and beyond Moscow and also decreases to the west to Pullman. The slope of the top of the basalt unit becomes greater west and southwest of Pullman. The top of the Grande Ronde Formation is lower under Palouse than at any other location within the Pullman-Moscow or Northern subareas. A map of the depth from land surface to the top of the Grande Ronde Formation was constructed using the map giving the elevation of the top of the Grande Ronde Formation (Figure 3-20) and data from a digital topographic map (Robischon, 2010a). The resulting map, presented as Figure 3-21, shows that the top of the Grande Ronde Formation is less than 50 feet below land surface along the channel of the South Fork of the Palouse River from Pullman to Albion and for a considerable distance along the Palouse River above Colfax.

3.2.5.4 Wanapum Formation The Wanapum Formation is the uppermost basalt unit over most of the Palouse Basin. The two members of the Wanapum Formation (Priest Rapids and Rosa) are shown in plan view on Figures 3-9 and 3-10 and are depicted on the various cross sections. The Priest Rapids member of the Wanapum Formation extends over essentially the entire portion of the Palouse Basin where basement rocks do not outcrop at land surface (Figure 3-10). The Roza member of the Wanapum Formation underlies the Priest Rapids member in the western portion of the Basin starting several miles west of Pullman and in the Elberton and Colfax areas (Figures 3-9 and 3- 11). The thickness of the Wanapum Formation within the Palouse Basin is small compared to the thickness of the Grande Ronde Formation.

3.2.5.5 Saddle Mountains Formation The Saddle Mountains Formation overlies the Priest Rapids Member of the Wanapum at several locations within the Palouse Basin. Figure 3-11 shows that Saddle Mountains basalt is present starting several miles west of Pullman. A very thin section of the Saddle Mountains Formation was penetrated in the IDWR well #4 and is shown on Figure 3-13.

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3.2.5.6 Structural Features Bush and Garwood (2005g) identify a sequence of northwest trending folds in the basalt sequence in the general vicinity of Pullman with additional folds in the Palouse, Elberton, and Colfax areas (Figure 3-1). Bush et al. (2001a, pages 5-6) present the following observations relative to the significance of the folds in the Pullman-Moscow area. “The nature of the interbeds in Pullman … suggests differential basining during basalt emplacement. The interbeds encountered in many of the wells in the Pullman area are interpreted as evidence of deposition in low areas… Columbia River basalt interbeds often represent deposition in deformation areas… The interbeds in the Pullman area are interpreted to represent deposition in minor ‘warps’ and not in erosional channels. Collectively, there is considerable evidence for folding during and after the emplacement of the upper Grande Ronde flows. The chemical results and correlations to other wells presented herein help verify that conclusion for the Pullman area… “It is believed that the PMB [Pullman-Moscow Basin] was a very complex area during basalt extrusion due to the interaction of pre-basalt highs, developing NW [northwest] trending folds and extensive subsidence to the west in the Pasco area during and after basalt extrusion… “The folds within the plateau of eastern Washington are commonly northwest trending and plunging, asymmetrical, low-amplitude, long wavelength features with wide synclinal areas separated by narrow anticlines and monoclonal ridges. Such folds are particularly difficult to locate and verify in the subsurface.” Among the conclusions stated by Bush et al. (2001a) are the following (pages 6 and 7). “A) The evidence is very strong for the presence of a synclinal warp in the upper Grande Ronde between Moscow and Pullman. “B) Correlations by Brown (1976), Heinemann (1994), and Provant (1995) indicate a downwarp in eastern Moscow. The downwarp could be from differential compaction of the Latah sediments in that area… “C) Elevation data at the base of the Wanapum 3,000 feet west of the Pullman well #7 shows that the top of the Grande Ronde rises approximately 80 feet in that distance. “D) Thinning of the Priest Rapids over Pullman adds to the evidence that an anticlinal high exists at the western edge of the town. “E) Topographic features and stream patterns in the Pullman area support the presence of an anticline west of Pullman… “K) Many of the complexities of the PMB are interpreted to be due to a differential basining near the influence of pre-basalt basement rocks with rugged topographic relief.” Bush (1996) provides additional insight relative to the geologic framework of the Pullman- Moscow portion of the Palouse Basin (pages 5 and 11). “The tectonic history of the region during and after basalt emplacement is important to understanding constraints on a subsurface model of the Moscow-Pullman basin. Tectonic activity in the Moscow-Pullman basin has been minimal since Priest Rapids flows covered most of the basin. However, considerable pre and post Priest Rapids subsidence

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beneath Lewiston and the Tri-cities areas of the Plateau affected distribution of numerous basalt flows. This subsidence created boundaries that separate the Moscow-Pullman basin from those regions geologically even though they are all underlain by similar basalt units. Most importantly is the existence of a geologic boundary at the west end of the basin extending from southwest of Chambers northwestward towards Albion… There are several changes that occur between east and west across this ‘zone’ or ‘lineament’. The evidence for a geologic boundary in that area is so compelling that the likely hood of a subsurface hydrological barrier that locality must be considered. A portion of the evidence is presented in list form.  Late Grande Ronde, pre-Priest Rapids subsidence caused several flows attempting to enter the Moscow-Pullman basin from the west to pinch or thin out over this area.  One member of the Wanapum Formation (Rosa Member) can be mapped at the surface and thinning from 200 feet in thickness to zero across this zone is documented. Thinning or pinching out of the late Grande Ronde and early Wanapum flows along the ‘zone’ indicates that the Moscow-Pullman basin was in part elevated from the Plateau proper during a major part of basalt emplacement history…  Well documented stratigraphic marker horizons in the basalt sequence that were once horizontal drop rapidly in elevation to the southwest across the ‘zone’ under discussion and indicate post-Priest Rapids deformation along that ‘zone’.  Well documented near vertical dike swarms of Grande Ronde Basalt located south of the area project into the ‘zone’ and could be present in the subsurface.  Gently folded post Priest Rapids flows southwest of Pullman have axis orientations that trend northwest and project into the ‘zone’ under discussion.  Modern streams in parts of Whitman County follow and parallel the Northwest trending ‘zone’.”

3.3 Hydrogeologic Framework

3.3.1 Introduction The hydrogeologic understanding of the Palouse Basin has grown from the initial report prepared by Russell in 1897 to studies conducted in the last 30 years by the USGS, state agencies, the two universities, and private entities. Many of the studies in recent years have been initiated and supported by a local water management entity, currently called the Palouse Basin Aquifer Committee (PBAC). This section of the report presents the hydrogeologic framework of the Basin.

3.3.2 Aquifer Identification and Temporal Growth of Knowledge

3.3.2.1 Aquifer Identification The geologic setting of the Columbia River Basalt Group along the east side of the Columbia Plateau creates a very complex hydrogeologic environment. Aquifers and aquitards in the basalt and sedimentary zones vary greatly over short distances. The water-producing intervals become less laterally continuous near the eastern edge of the Basin where basalt flows terminate and

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Palouse Ground Water Basin Framework Project FINAL report thick sequences of often fine-grained sediment are present. As is described above, the structural setting also appears to be more complex near outcrops of crystalline basement rock. Jones and Ross (1972, page 12) describe the deeper water-producing zones in the Moscow area as follows. “The lateral extent of the different aquifers is variable; therefore, hydraulic connection between nearby wells of similar depths is variable. In some places, water levels in a well will show considerable effect of pumping from a nearby well of similar depth; in other places, nearby wells will have little effect and more distant wells may have noticeable effect.” Barker (1979, pages 19-20) indicates the following relative to ground-water flow patterns in the Columbia River Basalt Group. “Faults, folds, and dikes in the basalt sequence are known to substantially affect the lateral movement of ground water in many areas of Eastern Washington. Such features can control water levels and impede, or even effectively block, ground-water movement… “Because there are many physical and structural variables affecting the occurrence and transmission of ground water in the basalt of the Columbia River Basalt Group, local circulation patterns can be extremely complex… “In spite of the complexities of basalt hydrology, the water-bearing zones can usually be divided into at least two general aquifer groups: an upper, shallow aquifer unit and a lower, deeper unit. This subdivision has been used in modeling the basalt aquifers in the Columbia Plateau … The subdivision has been based on the somewhat different aquifer characteristics and contrasting water-level patterns displayed by the two different depth intervals. The shallower aquifers are cut locally by canyons or other surface depressions so that their areal extent is limited and they are not generally connected to significant sources of lateral recharge. The deeper aquifers are generally continuous areally over greater distances than are the shallower aquifers and are usually the more productive. These deeper aquifers typically comprise the regional flow system and are often referred to collectively … as the primary aquifer system.” In general terms, the Grande Ronde Basalt Formation hosts the lower aquifer system that is the dominant water-supply source for municipalities in the Palouse Basin. All of the large production wells for WSU, UI, and Pullman plus most of the large production wells for Moscow are completed in the lower aquifer (Figure 3-22). Water supply wells for the cities of Palouse and Colfax are also completed within the Grande Ronde Formation. Later portions of this chapter address the potential hydraulic connection of the lower aquifer in the Pullman-Moscow subarea with the same aquifer in the Northern subarea (city of Palouse) and the Western subarea (cities of Colfax and Garfield). In general terms, the Wanapum Basalt Formation and the underlying Vantage Formation sediments host the upper aquifer that is the primary water-supply source for domestic and other small yield wells plus several water-supply wells for Moscow and UI. The areal extent of water- producing zones in this aquifer is limited in the Western subarea and the western portion of the Pullman-Moscow subarea because the aquifer is cut locally by stream valleys. The upper aquifer has its greatest thickness, lateral extent, and importance as a water supply source in the Moscow

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Palouse Ground Water Basin Framework Project FINAL report portion of the Pullman-Moscow subarea and in the Northern subarea near the city of Palouse. In these areas the contact between the Wanapum Formation and the underlying Grande Ronde Formation occurs at a lower elevation and the upper aquifer is much thicker and is not cut by stream channels.

3.3.2.2 Temporal Growth of Knowledge of the Aquifers Significant steps in the growth of knowledge of the hydrogeology of the Palouse Basin are summarized in this portion of the report. The sequential growth of knowledge has led to changing hydrogeologic conceptual models.  Russell (1897) published the first hydrogeologic report that included the Palouse Basin. He documents that flowing wells had been drilled in the canyon of the South Fork of the Palouse River at Pullman in the early 1890s. The wells were in the depth range of 70 feet to 90 feet and penetrated basalt, clay, and sand zones. Russell notes that the static water- level elevation in wells drilled higher on the sides of the canyon was about 2,365 feet. He also reports that wells drilled to a depth of about 100 feet in Moscow flowed at land surface when originally drilled in 1890. The water level in Moscow was 8 to 9 feet below land surface by 1896.  Landes (1905) provides an overview of the Whitman County ground-water supply. Colfax has wells ranging from 12 to 120 feet deep; water was found at approximately 40 feet below land surface. No flowing wells existed. In the Pullman area, well depths range from 100 to 130 feet deep; water was found at about 100 feet below land surface and derived from the beds of sand. Landes notes that the wells did not flow as strongly as they did in the past. The city of Pullman had two wells; one drilled in 1890 and one in 1899. Both wells were located near the stream bed, had a bottom depth of 120 feet, had well head elevation of 2,341 feet, flowed at last surface to a height of 19 feet, and had decreasing supply over time. The city of Palouse had several wells ranging in depth from 100 to 300 feet. Depth to the primary water source was 150 feet. Water was derived from the sand. Some wells flowed at land surface and others did not. There was no seasonal variation of the water levels.  The Laney et al. (1923) report is focused on the ground-water supply in Moscow. Apparently based on the belief that basalt yields only small amounts of water, they postulate that the “main or parent” aquifer is the unconsolidated sediment immediately overlying the granite at depth. No wells penetrated this aquifer in 1923. “Secondary aquifers” are identified in both basalt and sand at approximate depths of 90 feet and 160 feet (upper aquifer). Laney et al. document that a city well believed to be completed in the lower of the “secondary” aquifers had flowed when drilled in 1895 but had a depth to water of 44 feet in the 1920s when it was measured. They calculate an annual recharge rate of about 1.3 inches based on a water balance approach, which yields about 550 million gallons per year of recharge over the Moscow area. The estimated annual groundwater use in 1923 was about 230 million gallons.  Foxworthy and Washburn (1963) conducted a ground-water supply study for the Pullman area. Two aquifer zones in the elevation interval of 2,170 to 2,290 feet (50 to 170 feet below ground in downtown) are the primary water source for the Pullman area (lower aquifer). They conclude that only a fraction of the average 21 inches of precipitation

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reaches the aquifer. They also conclude that the basalt is recharged from streams and from downward percolation from the loess. The principal discharge from the artesian aquifers is discharge from wells and seepage to streams. Foxworthy and Washburn conclude that the gradual decline in the ground-water level has increased recharge to the aquifer. They recognize that Moscow and Pullman are in separate hydrologic sub-basins based on differences in water-level elevation and rates of water-level decline. Finally, they indicate that the most feasible method for artificially recharging the Pullman artesian zone is by direct injection of water into wells during part of the year and pumping those wells during the remaining time.  Walters and Glancy (1969) report on the geology and ground-water resources of Whitman County. They indicate that wells can yield 1,000 gallons per minute or more almost everywhere in Whitman County if they are drilled deep enough into the basalt. The yield depends on the number of flows penetrated. Walters and Glancy indicate that the average yield increased approximately 125 to 200 gallons per minute for each additional 100 feet of penetration below the water table. They note that, except for Pullman, ground-water levels fluctuate in response to cyclic climatic conditions with no pattern of long-term water-level decline.  The Jones and Ross (1972) hydrogeologic assessment of the Moscow area was conducted after construction of the first group of deep wells (UI well #3 and Moscow wells #6 and #8). They divide the penetrated thickness of about 1,500 feet of sediment and basalt that overlie the crystalline rock into three hydrostratigraphic units. Each zone consists of basalt and interfingering sediment. The upper artesian zone includes all wells constructed prior to the early 1960s (upper aquifer). According to Jones and Ross, UI well #3 is completed in the middle artesian zone, with Moscow wells #6 and #8 completed in the lower artesian zone (the middle and lower artesian zones are part of the lower aquifer). Based on the Jones and Ross approach, the middle artesian zone includes the elevation range of about 1,700 feet to 2,050 feet, with the upper artesian zone above 2,050 feet and the lower artesian zone below an elevation of about 1,700 feet. Jones and Ross document that there had been about 120 feet of water-level decline in what they called the upper artesian zone prior to switching the water production at both Moscow and UI to deeper aquifers in the 1960s. Jones and Ross conclude that pumpage was not in excess of recharge in the upper artesian zone during the period of 1896 to 1960. This conclusion is based on: 1) the fact that near surface ground-water levels remained constant even though ground-water levels in the upper artesian aquifer declined, and 2) the results of operation of an analytical model using image well theory.  Luzier and Burt (1974) describe hydrogeologic similarities between the Pullman area and the Odessa area in central Washington. In both areas, the upper part of the basalt contains aquifer zones of relatively small yields and high hydraulic head whereas deeper zones have lower hydraulic head and higher yields. Luzier and Burt note that there is essentially no vertical gradient within the Grande Ronde Formation in the Pullman area; water-level elevations are very similar in both deep and shallow wells. They also conclude that the water-level decline was about the same away from pumping centers as near pumping centers.

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 Brown (1976) describes information gained from the construction of the WDOE test well, located midway between Moscow and Pullman. He indicates that the water-level change that marks the transition from the upper to the lower aquifers occurs at a depth of about 200 feet (elevation of about 2,275 feet). Rock chemistry data show that the top of the lower Yakima basalt (Grande Ronde Formation) at this site occurs at a depth of about 90 feet (elevation of about 2,385 feet). This indicates that the transition between the upper aquifer and the lower aquifer occurs near the bottom of the uppermost basalt flow of the Grande Ronde Formation at this location. Brown shows that the static depth to water remained approximately constant in the Grande Ronde Formation during drilling in the depth range of 562 feet to the bottom of the well at 982 feet. This indicates that there was essentially no vertical hydraulic gradient in this portion of the lower aquifer.  Barker (1979) constructed the first numerical ground-water model of the Pullman- Moscow subarea. In support of this effort, he conducted a mass measurement of water levels in wells and summarized hydrogeologic knowledge of the area. The single-layer model he constructed represents the primary or deep aquifer that he assumed was common to both Moscow and Pullman (lower aquifer). Barker includes a partial barrier to ground-water flow located west of Pullman in his numerical model representation of the aquifer. His evidence for this partial barrier is as follows: 1) the water-level elevation in the Grande Ronde Formation is approximately the same regardless of well location or well depth, and 2) the rate of temporal water-level decline is uniform across the area. Barker’s “barrier zone” restricts flow only in the lower aquifer. Vertical leakage from the upper aquifer was found to be the most significant source of recharge. Barker calibrated his model to historical water-level declines using historical pumping data.  Wyatt-Jaykim and Ralston (1987) describe the construction of WSU well #7 including the test hole drilled to explore geologic and hydrologic conditions at depth. The upper 1,000 feet of the well was constructed as a production well for WSU and was cased and screened. An uncased test well was constructed out of the bottom of the production well in the depth range of 1,000 feet to 2,224 feet in an effort to understand water productivity deeper within the Grande Ronde Formation. Major water producing zones were intercepted at depths of about 560, 680, and 920 feet within the production well. Small yield water producing zones were encountered in the lower portion of the well at depths of 1,590, 1,750, 1,850, and 1,950 feet. The 1,590- and 1,850-foot zones were composed of sediment, predominantly granitic sand. Water-level data obtained during drilling suggest that a 5-foot drop in water levels occurred between the depths of 1,820 and 1,943 feet. A grout seal was placed in the uncased test hole at a depth of about 1,814 feet to prevent downward flow within the borehole. Bush (2005d) subsequently determined that the contact between the Grande Ronde Formation and the underlying Imnaha Formation at this site occurs at a depth of about 1,600 feet. No large-yield zones were penetrated below a depth of about 1,000 feet. Thus, data collected from WSU well #7 indicate that there is little water productivity within the Grande Ronde Formation below a depth of about 1,000 feet at that location.  Lum et al. (1990) constructed the second numerical ground-water model of the area. Their model included the Palouse Basin (as described and shown in Chapter 1 of this report) plus an area along the Snake River to the southeast. Lum et al. compiled hydrogeologic knowledge of their study area and also conducted a mass measurement of

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water levels in many of the same wells that were measured by Barker (1979). The Lum et al. (1990) numerical model includes three layers with which they represented the loess, the Wanapum aquifer (upper aquifer), and the Grande Ronde aquifer (lower aquifer). Lum et al. could not find any specific features related to the “barrier zone” identified by Barker (1979) and thus did not directly include it in the numerical model. However, Lum et al. (1990) did include a lower hydraulic conductivity zone within the lower aquifer west of Pullman in a similar area as Barker’s “barrier zone”. Lum et al. (1990) calibrated their model to historical water-level declines using historical pumping data.  Heinemann (1994) evaluated the hydrogeologic setting along selected streams within the Palouse Basin in order to gain a greater understanding of surface-water/ground-water interaction. He concludes that significant ground-water discharge to streams only occurs in the central portion of Union Flat Creek and the upper reach of the Palouse River. Heinemann also indicates that the South Fork of the Palouse River does not receive significant ground-water discharge.  Leek (2006) developed a GIS database for the Palouse Basin and evaluated available hydrogeologic information. She prepared several hydrogeologic cross sections and water-level contour maps for the upper and lower aquifers.  Fairley et al. (2006) evaluate the potential for ground water recharge to the upper aquifer through sediments along the granite/basalt contact in the vicinity of Moscow Mountain. They conclude that recharge is limited by thick, low permeability sediments and the poor connectivity between the Priest Rapids basalt and the overlying sediment.  The hydraulic characteristics of the Grande Ronde and Wanapum Formations have been evaluated in a number of UI theses directed by Dr. Jim Osiensky. These include: Owsley, 2003; Badon, 2007; McVay, 2007; Bennett, 2009; and Fiedler, 2009. The individual contributions of these reports are included later in this section.

3.3.3 Characteristics of the Lower Aquifer The top of the lower aquifer at sites within the Pullman-Moscow subarea is identified during well construction by a significant drop in water level. Wells completed in the upper aquifer have higher ground-water levels as compared to wells completed in the lower aquifer. The drop in water level showing the transition from the upper aquifer to the lower aquifer occurs near the bottom of the uppermost Grande Ronde basalt flow at the DOE test well (Brown, 1976). The aquitard separating the two aquifers is a combination of the sedimentary interbed (Vantage member of the Latah Formation) and the dense interior of the uppermost basalt flow of the Grande Ronde Formation. The top of the lower aquifer is less well-defined at other locations, particularly in the Pullman area. The bottom of the lower aquifer has not been well defined but is assumed to be approximately equivalent to the bottom of the Grande Ronde Formation. The Grande Ronde Formation is underlain by the Imnaha Formation in the western portion of the Pullman-Moscow subarea and by a combination of sediment and metaphoric rock in the eastern portion of the subarea.

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3.3.3.1 Water-Producing Zones Water-producing zones in the Grande Ronde Formation occur dominantly along contact zones between overlying and underlying individual basalt flows within the formation. There are a few instances in the Moscow area (Moscow wells #6, 8, and 9) where wells completed in Grande Ronde Basalt obtain significant quantities of water from sedimentary zones between the basalt flows. The centers of basalt flows tend to be dense and act as aquitards. Many of the sedimentary interbeds are composed of clay and/or silt and also act as aquitards. Identification of water-producing zones is based on data collected during well drilling and on borehole geophysical logs. Golder (2001, page 10) lists the following field evidence for water- producing zones.  An increase in water production at the time of drilling;  Zones of highly fractured basalt;  A contact between basalt and sedimentary interbeds (indicating a flow top and bottom zone);  Increased borehole width which indicates zones of less competent, fractured rock;  Electrical conductivity changes in the rock of the borehole walls which may indicate water inflow to the borehole; and  Fluid temperature changes that may indicate water inflow to the borehole. All of the production wells completed in the lower aquifer in the Pullman-Moscow area penetrate more than one water-production zone. For example, screens were placed opposite three zones of significant water production in Pullman well #7: 277-360 feet, 470-495 feet, and 680-720 feet (Golder, 2001, page 10). As a comparison, screens were set opposite the following water- producing zones in Pullman well #8: 327-355 feet, 440-450 feet, 516-533 feet, 555-570 feet, 585-596 feet, 611-718 feet, and 752-793 feet (Anderson et al., 2008). Table 3-1 shows construction information on production wells in the Basin. The locations of wells with known latitude and longitude are shown on Figure 3-22a. The yield of a given well, such as Pullman well #7 or Pullman well #8, is the summation of the amount of water obtained from each of the water-production zones for which the well has screened or open-hole sections. In the same way, the static water-level elevation of the well is a yield-weighted average of the water-production zones across which the well is completed. Small changes in hydraulic head in different water-production zones screened in a given well can result in vertical flow within the borehole. Golder (2001, page 9) describes how information from a temperature log can be analyzed relative to vertical flow within a well. “In Pullman Well No. 7, there is an exponential increase in temperature from the surface to a depth of 500 feet below the top of the casing. At this depth there is an abrupt … increase in temperature… The depth of this temperature discontinuity corresponds to the depth of an interpreted fracture and water-producing zone from the caliper, video logs and resistivity logs. This temperature discontinuity is interpreted to be a result of cooler water entering the borehole from the region immediately shallower than 500 feet. At a depth between 600 and 650 feet bgs [below ground surface], warmer temperatures were

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encountered. This may be the result of warmer water entering the borehole from fractures between these depths”. Water-level data collected during drilling are not presented by Golder (2001) for Pullman well #7. The flow within the borehole between the water-producing zones at 470- 495 feet and 680-720 feet may represent only a small change in ground-water level elevation. The water producing zones in the Grande Ronde Formation are grouped together as the lower aquifer for this study. This designation is based on two aspects of the water-level data set for the Pullman-Moscow subarea. First, the static water-level elevation is very similar for wells completed at different depths within the Grande Ronde Formation. Second, the temporal rate of water-level decline is approximately the same for wells completed at different depths within the Grande Ronde Formation. These data indicate that the different water-producing zones act as a single aquifer when considered over long time periods. The water-producing zones may not appear to be hydraulically interconnected during short time periods, such as during an aquifer test. The lower aquifer also is present in the Northern and Western subareas of the Palouse Basin. The characteristics of the aquifer in these areas are poorly understood because of the paucity of deep wells. The City of Palouse wells provide data on the lower aquifer in the Northern subarea while wells for the cities of Colfax and Garfield provide information in the Western subarea.

3.3.3.2 Hydraulic Characteristics A number of aquifer tests have been conducted within the Pullman-Moscow subarea of the Palouse Basin. Many of the tests were conducted to obtain yield information for recently completed production wells. Other tests were conducted to evaluate the horizontal and vertical hydraulic continuity of water-producing zones within the Grande Ronde Formation. Values of aquifer parameters (transmissivity and storativity) calculated from the aquifer tests depend not only on the hydraulic characteristics of the tested aquifer but also on the construction and completion of both the pumping well and the observation well. Thus, it is difficult to compare transmissivity and storativity values calculated by different authors using data obtained from different aquifer tests. The aquifer coefficients used in the calibrated numerical models constructed by Barker (1979) and Lum et al. (1990) probably are the best representation of aquifer parameters for the lower aquifer. Often the product of primary importance from aquifer tests is improved understanding of the aquifer continuity and boundaries. Graduate students at UI, under the guidance of Dr. Jim Osiensky, have conducted and are continuing to conduct large-scale aquifer tests in an effort to gain a greater understanding of the hydraulic characteristics of the Grande Ronde aquifer in the Pullman-Moscow subarea. The following paragraphs provide information gained from aquifer test studies conducted by Owsley (2003) and McVay (2007). Owsley (2003, pages 14-17) describes the characteristics of the Grande Ronde aquifer based on a testing program that he conducted as follows. “The four aquifer tests conducted for this study identified hydraulic connections through various wells. These connections were then correlated with the geologic cross section … to identify potential aquifer boundaries. Figures … suggest that the Moscow-Pullman basin has at least three separate Grande Ronde aquifers that, hydraulically, are poorly connected…

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“Aquifer MGR1 [Moscow Grande Ronde aquifer #1] is a highly fractured basalt zone that ranges from 100 to 150 feet thick. The elevation of this aquifer ranges from 1750 to 1920 feet above mean sea level in the Moscow vicinity. [A figure] … shows that this aquifer extends to the west to at least the WDOE test well, but not much further.... U of I well #4 and Moscow well #9 are completed in this aquifer. “Aquifer MGR2 [Moscow Grande Ronde aquifer #2]... is [the] bottommost aquifer of the region, located between 1350 and 1650 feet above mean sea level. This aquifer is composed of 250 feet of basalt flows and 50 feet of sediments. This aquifer extends westward to at least the WDOE test well; however, a lack of data precluded further extrapolation… The City of Moscow wells #8 and #6 are completed in this aquifer. “Aquifer PGR1 [Pullman Grande Ronde aquifer #1] is the only aquifer delineated in the Pullman pumping center. This aquifer is composed entirely of 200 feet of basalt flows. The aquifer is located between 1700 and 1900 feet above mean sea level in the Moscow [Pullman] region. This aquifer extends northward to the city of Palouse through the gap between Angel Butte and Kamiak Butte. Both MGR1 and PGR1 appear to extend through the gap; however, is not suspected that MGR1 and PGR1 have a strong hydraulic connection. The western and southern boundaries of PGR1 are still undefined…” Owsley’s (2003) statements contrast with the findings of Holom (2006) who, using his gravity data, determined that the Grande Ronde Formation did not extend through the Kamiak Butte – Angel Butte gap. Owsley (2003, page 50) concluded the following from his study. “The Grande Ronde aquifer system is very heterogeneous due to the irregular nature of interflow zones, basalt/sediment interfaces, merged basalt lobes, and complex basalt/crystalline rock contacts. “The Grande Ronde aquifer system is composed of multiple, hydraulically compartmentalized aquifers that appear to be hydraulically separated on the short term (e.g. aquifer tests). “Pumping Grande Ronde wells in the Moscow pumping center does not affect the water levels in Grande Ronde wells in the Pullman pumping center during short-term tests. “Hydraulic connections exist between City of Palouse well #2 [should be well #3] and the Moscow and Pullman pumping centers through the Angel Butte/Kamiak Butte gap during separate, short term, aquifer tests.” McVay (2007, page 113) provides the following conclusions based on the results of two additional aquifer tests that he conducted. “The Grande Ronde aquifer is composed of a system of individual, yet hydraulically connected aquifers separated by aquitards (i.e. a multi-aquifer system). Aquifer testing has indicated hydraulic connection among the aquifers beneath Moscow, Pullman and Palouse… “The combination of the large distance between Moscow and Palouse, aquifer heterogeneity, and complex boundary conditions prevented measurable Moscow- generated drawdown in the Palouse wells during the January 31, 2006 aquifer test. However, Pullman area pumping effects were observed in well PAL_1 [Palouse well #1]

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which, because of the observed communication between Moscow and Pullman wells, provide evidence for hydraulic connection between these three areas of the basin.” McVay (2007, page 115) also concludes the following. “The Palouse Basin consists of several geologically distinct sub-basins. Variable hydrogeologic properties within these geologic regimes cause short-term differences in hydraulic behavior. This heterogeneity combined with superposed cones of depressed formed by pumping centers causes ‘apparent’ hydraulic separation spatially and temporally, but does not prevent hydraulic connection from one side of the basin to the other over the long-term.” Golder (2001) provides the results of an aquifer test conducted using Pullman well #7 as the pumping well with water-level measurements taken in the following observation wells: Pullman wells #2, 3, 4, and 5 and the WSU test well. In addition to the pumping well, drawdown was measured only in the two closest observation wells: Pullman well #2 at a distance of 40 feet and Pullman well #4 at a distance of 60 feet. The 48-hour test with a pumping rate of about 3,200 gallons per minute did not cause measurable drawdown in any of the other observation wells. Golder (2001) did note that drawdown in Pullman wells #2 and #4 was evident from the pumping of WSU well #7, located about 3,300 feet away. The results of aquifer tests conducted using newly constructed Pullman well #8 are described by a Golder Associates report (Anderson et al., 2008). Drawdown was detected in Pullman well #3 with a small amount of drawdown detected in Pullman well #6. The effect of pumping Pullman well #8 was not detected in Pullman wells #7 and #5 and in the WSU test well (well #1). The authors noted that a negative boundary was detected based on the drawdown data from well #8. A negative boundary represents a significant decrease in aquifer transmissivity. Anderson et al. (2008) estimated that the distance from well #8 to the boundary is approximately 3,200 feet. Several authors note that pumping a well completed in a deeper portion of the lower aquifer can cause drawdown in nearby wells that are completed opposite shallower water-producing zones in the aquifer. For example, Golder (2001) documented that pumping Pullman well #7 (elevation of screened interval 1,622-2,066 feet) caused drawdown in Pullman well #2 (elevation of screened interval of 2,111-2,209 feet). McVay (2007) identified drawdown in the relatively shallow Champion Electric well from the combined operation of UI well #3 and Moscow well #9. McVay (2007, page 95) noted the following: “The Champ [Champion Electric] well responds much later than the more distant (from M_9 and UI_3) DOE well… The delay and magnitude of drawdown in this well suggest that Champion well is hydraulically insulated, but not isolated, from the Moscow wells by a leaky aquitard.” These aquifer-test results indicate that there is some degree of vertical hydraulic connection between water-producing zones within the lower aquifer. The productivity of production wells within the Pullman-Moscow area, as measured by specific capacity, varied widely. Specific capacity, which is the discharge divided by drawdown, is a lumped parameter that includes aquifer hydraulic conductivity but also the number of water- producing zones penetrated by the well, the drilling methodology used, and the hydraulic efficiency of the well. Table 3-1 presents well construction and specific capacity information on

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Palouse Ground Water Basin Framework Project FINAL report production wells in Pullman and Moscow respectively. The specific capacity values shown on the tables illustrate that the lower aquifer is highly productive. Information on the hydraulic characteristics of the lower aquifer in the Northern subarea is derived from an aquifer test on City of Palouse wells conducted by Ralston (2000). Palouse well #3 (Ralston lists name as well #2) was pumped at a rate of about 800 gallons per minute with about 2.5 feet of drawdown in the pumping well and 0.3 feet of drawdown in Palouse well #1. Aquifer test data indicate the presence of negative hydraulic boundaries, probably the contact of the basalt with the crystalline basement rocks. Essentially no information is available relative to hydraulic characteristics of the lower aquifer in Colfax or Garfield in the Western subarea.

3.3.3.3 Aquifer Boundaries Aquifer boundaries are described for each of the three subareas that make up the Palouse Basin: Pullman-Moscow, Northern (includes city of Palouse), and Western (includes Colfax and Garfield). The Pullman-Moscow and Northern subareas are similar with respect to being bounded mostly by crystalline rock. The Western subarea is bounded crystalline rock only on the east. 3.3.3.3.1 Pullman-Moscow Subarea Crystalline rock outcrops form the boundary for most of the perimeter of the Pullman-Moscow subarea (Figure 3-1). The lower aquifer covers a smaller area than is shown on Figure 3-1 because Grande Ronde basalt does not extend fully to where the crystalline rock currently outcrops. As is described in Section 3.2 Geologic Framework, mostly fine-grained sediment is present at the eastern terminus of the basalt flows because the basalt dammed the drainages and sediment deposition was dominantly in ponds and lakes. Three areas exhibit gaps in the enclosure of crystalline rock around the Pullman-Moscow subarea. The largest gap is southwest of Pullman between the crystalline rock exposures near Albion and near Chambers (Figure 3-1). The next biggest gap is between Kamiak Butte and Angel Butte north of Pullman. The smallest gap is where Four Mile Creek flows between Kamiak Butte and Smoot Hill north-northeast of Albion. The potential for ground water to flow into or out of the Pullman-Moscow subarea via the lower aquifer through each of these three gaps is evaluated in the following paragraphs. There appears to be little doubt that the Grande Ronde Formation is laterally continuous in an east-west direction in the gap between crystalline-rock outcrops near Albion and near Chambers. An east-west geologic cross section prepared by Bush (2005c) and presented in Figure 3-11a shows lateral continuity in the R1, N1, R2, and N2 members of the Grande Ronde Formation west of Pullman. However, as described in Section 2.0, there is evidence to suggest that the Grande Ronde Basalt is thinner and perhaps structurally deformed in the Albion-Chambers gap area. Geologic features in this area likely result in a zone of restricted ground-water flow. Bush (1996, page 5) describes the area as follows. “Tectonic activity in the Moscow-Pullman basin has been minimal since Priest Rapids flows covered most of the basin. However, considerable pre and post Priest Rapids subsidence beneath Lewiston and the Tri-cities areas of the Plateau affected distribution of numerous basalt flows. This subsidence created boundaries that separate the Moscow- Pullman basin from those regions geologically even though they are all underlain by

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similar basalt units. Most importantly is the existence of a geologic boundary at the west end of the basin extending from southwest of Chambers northwestward towards Albion… There are several changes that occur between east and west across this ‘zone’ or ‘lineament’. The evidence for a geologic boundary in that area is so compelling that the likely hood of a subsurface hydrological barrier that that locality must be considered.” Barker (1979) uses reduced transmissivity to represent a “barrier zone” in his numerical model in a northwest trending area west of Pullman and south of Albion. The solid – dotted line on Figure 3-23 is the east side of the “barrier zone” as delineated by Barker. The line trends from a site located west of Chambers in a northwest direction to a site located west of Albion. Lum et al. (1990) could not find geologic evidence for the “barrier zone” of Barker (1979). However, the hydraulic conductivity representation of this portion of the Basin is similar in the numerical models constructed by Barker (1979) and Lum et al. (1990). Representation of the lower aquifer in the two numerical models is described in Section 3.5. Geophysical studies provide conflicting evidence of whether the Grande Ronde Formation is laterally continuous in a north-south direction in the gap between crystalline-rock outcrops between Kamiak Butte and Angel Butte. Holom (2007) concluded that crystalline rock is relatively shallow in the gap and that basalt flows of the Grande Ronde Formation are not present. On the other hand, Klein et al. (1987) indicate that the depth to crystalline rock in the gap is sufficient to allow Grande Ronde basalt to be present. Several investigators have concluded that Palouse city wells completed in the lower aquifer respond to pumping of wells in Pullman and possibly Moscow (e.g., Owsley 2003). In addition, the similarity of water-level elevation and the rate of water-level decline in the Palouse and Pullman-Moscow areas support the concept of a hydraulic connection in the gap. Water-level data are described later in this chapter. The hydrologic evidence supports Klein et al. (1987) that at least the upper portion of the Grande Ronde Formation is laterally continuous through the gap. The only alternative is that complicated hydrology exists in which water takes another route allowing a hydrologic connection between the City of Palouse wells and wells in the Pullman-Moscow subarea. The presence of the Grande Ronde aquifer in the gap between Kamiak Butte and Smoot Hill where Four Mile Creek flows to the west is unlikely but is still an open question. The structural contour map for the top of the Grande Ronde Formation shows an elevation of 2,300 feet on the east side of the gap and 2,250 feet on the west side of the gap (Figure 3-20b). The elevation of the top of the crystalline rock is shown as greater than 2,000 feet through the gap area (Figure 3- 4). Bush and Garwood (2005b) show three reference wells in the gap area on their geologic map of the Albion quadrangle. The well table that accompanies the geologic map shows that the top of the Grande Ronde Formation was picked by Heinemann (1994) in one of the three wells. 3.3.3.3.2 Northern Subarea Crystalline rock outcrops form the boundary for most of the perimeter of the Northern subarea (Figure 3-1). In additional to the gap between Kamiak Butte and Angel Butte, a bedrock gap is oriented north-northeast to south-southwest midway between Palouse and Elberton. This gap forms the boundary between the Northern subarea and the Western subarea. There appears to be little doubt that the Grande Ronde Formation is laterally continuous in an east-west direction through this gap between crystalline-rock outcrops near Palouse and Elberton. The panel diagram presented in Figure 3-12 shows lateral continuity in the Grande Ronde Formation in this area. Little hydrogeologic information is available for the Palouse to Elberton portion of the

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Basin. There is also a small gap between bedrock outcrops along the east side of the Palouse sub-basin near Potlatch. The potential for ground-water inflow through this gap is very limited because the gap is narrow. 3.3.3.3.3 Western Subarea The Western subarea is located west of most of the crystalline rock outcrops along the east side of the Columbia Plateau. The potential exists for ground-water inflow from the Pullman- Moscow subarea via the Albion to Chambers gap and possibly the Four Mile Creek gap. Ground water may also enter the Western subarea via the gap between Palouse and Elberton. The western boundary of the Western subarea is unknown. The basalt units likely are laterally continuous west of Colfax into the expanse of the Columbia Plateau. Structural features may be important in limiting ground-water flow along the western side of the Western subarea, but they have not been identified to date.

3.3.3.4 Horizontal and Vertical Hydraulic Gradients Numerous authors have noted that there are only small differences in water-level elevation between water-producing zones within the lower aquifer in the Pullman-Moscow subarea. Barker (1979) illustrated the issue of vertical gradient in what he called the primary aquifer (lower aquifer) in a plot of the altitude of water level as measured in 1974 against the altitude of the bottom of the well (reproduced as Figure 3-24). The plot shows that water-level elevation is proportional to well depth until the primary aquifer (lower aquifer) is penetrated. Figure 3-24 shows that there is very little difference in water-level elevation regardless of the depth into the lower aquifer that the wells are constructed. Deep wells drilled since 1974 show the same pattern of water-level elevations. This means that vertical hydraulic gradients are small within the lower aquifer within the Pullman-Moscow subarea. Water-level elevations in wells completed in the lower aquifer are approximately the same, regardless of location within the Pullman-Moscow subarea. This is illustrated by data collected as part of a mass measurement of water levels in the 1970s by Barker (1979) (Figure 3-23). Current water-level data from wells completed in the lower aquifer show the same general pattern. The 2009 water-level elevations of wells completed in the Grande Ronde Formation in the Pullman-Moscow sub-basin ranged from 2,234 feet to 2,263 feet, without an areal trend (Snyder and Haynes, 2010). Based on available information, there is no consistent hydraulic gradient to indicate the direction of horizontal ground-water flow within the lower aquifer in the Pullman-Moscow subarea. Essentially no information on horizontal or vertical hydraulic gradients is available for the Northern and Western subareas. This is because of the paucity of wells completed in the Grande Ronde Formation in these areas.

3.3.3.5 Temporal Water-Level Changes Ground-water levels in the lower aquifer in the Pullman-Moscow sub-basin have been declining for more than 70 years. Water-level data are available for the WSU Test Well (well #1) since 1935 (Figure 3-25). The approximate rate of water-level decline for selected periods based on a regression analysis is given below for the WSU Test Well (Robischon, personal communication, 2010):

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 1935 to 1963 0.7 feet per year  1945 to 1961 1.45 feet per year  1965 to 1981 1.77 feet per year  1963 to 1985 1.7 feet per year  1985 to 1995 1.4 feet per year  1995 to 2007 0.86 feet per year The construction and operation of production wells completed in the lower aquifer in the mid 1960s in Moscow appears to have caused an increase in the rate of water-level decline in the WSU Test Well. These results seem to confirm that the three wells drilled at that time into the lower aquifer (Moscow wells #6 and #8 and UI well #3) are hydraulically part of the same aquifer that is penetrated by the WSU Test Well. The decreased rate of water-level decline after 1995 is likely the result of a stabilization and ultimately a reduction in pumping by the entities as guided by the 1992 Ground Water Management Plan. The water-level decline evident in the WSU Test Well occurred in all of the wells completed in the lower aquifer within the Pullman-Moscow subarea. Figure 3-26 shows that hydrographs for production and monitor wells in the Pullman-Moscow subarea that are completed in the lower aquifer are very similar. Note that the lower aquifer is designated “Grande Ronde” and the upper aquifer is designated “Wanapum” on Figure 3-26. Historical water levels are available for City of Palouse wells located in the Northern subarea that are completed in the lower aquifer. Data from one of the Palouse wells are included in Figure 3-27 along with selected Pullman wells. The water-level elevation and the rate of water- level decline for the City of Palouse well are very similar to characteristics for wells in Pullman (PBAC 2001). PBAC (2000, page 23) describes the Palouse well data as follows. “Comparison of the historic groundwater [sic] level elevation declines at the cities [Pullman and Moscow] and universities [WSU and UI] to the Palouse well show similar rates of decline. However, while the cities and universities have increased pumpage since 1986, Palouse has significantly decreased the amount of groundwater [sic] pumped annually… Despite decreasing pumpage, water levels in Palouse continue to decline at a rate similar to the rates of decline in the Pullman and Moscow area municipal wells. These data support the theory that the Palouse area north of Kamiak Butte is hydraulically connected to the Pullman-Moscow groundwater [sic] basin and that pumpage from the Grande Ronde aquifer [lower aquifer] at the Pullman and Moscow city centers are affecting groundwater [sic] levels in city of Palouse.” Information on the lower aquifer in the Western subarea is limited primarily to data from Colfax and Garfield water supply wells. The Glenwood flowing wells are located about 6 miles northeast of Colfax at an elevation of about 2,090 feet and supply water for the city. These wells have a reported depth of 105 feet and 110 feet and were drilled in the early 1900s. No decline of well yield has been reported. Two deep wells were drilled in the period 1949 to 1954 within the city of Colfax to depths of 595 feet and 723 feet. No water-level decline has been reported for these wells although very few readings are available. Two data loggers have been installed in

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Palouse Ground Water Basin Framework Project FINAL report the Colfax wells. The Clay Street data logger has recently been installed; there have been issues with the data logger installed in one of the Glenwood wells. . Limited information is available for the four wells that have been drilled for the City of Garfield. Based on records, mostly from the City, well #1 was drilled in 1907 to a depth of 350 feet and is now abandoned. Well #2 was also drilled in 1907 to a depth of about 245 feet. This well still exists but is not used as a supply source for the city. Well #3 was drilled in 1946 to an unknown depth. The well provides about 500 gallons per minute of the supply for the city. Well #4 was drilled in 1989 to a depth of 315 feet, according to a well driller’s report. The reported yield is 350 gallons per minute. The static depth to water of well #4 was measured as about 108 feet on June 10, 2010. The well driller’s report shows a depth to water of 75 feet at the time the well was drilled. The accuracy of this measurement is not known.

3.3.4 Characteristics of the Upper Aquifer The upper aquifer occurs in basalt and sediment and is present at essentially all locations within the Palouse Basin where crystalline rock does not outcrop. The aquifer is thickest and has the highest percentage of sediment within the eastern portion of the Pullman-Moscow subarea and the east portion of the Northern subarea. The upper aquifer is composed almost entirely of basalt and is partially to entirely cut by stream valleys in the western portion of the Pullman-Moscow subarea, the western portion of the Northern subarea, and most of the Western subarea.

3.3.4.1 Water Producing Zones Badon (2007, page 18) describes the upper aquifer in the general Moscow area as follows. “The producing zones in the Wanapum aquifer [upper aquifer] system include sand and gravel portions of the Vantage equivalent interbed as well as fractures in the basalt. The sand and gravels portions of the Vantage equivalent are thought to be channel deposits of Miocene streams; these deposits occur along the eastern margins of the basin, and in the center of the city of Moscow… These coarse deposits grade into clay and thin toward the west. Groundwater [sic] in the Wanapum aquifer [upper aquifer] system is also believed to be produced from fractured zones near the top and bottom of the Lolo flow (of the Priest Rapids Member)…” The upper aquifer consists mostly of basalt, flow-contact water-producing zones west of Moscow within the Palouse Basin. Stream valleys are incised into the Wanapum Formation and lateral ground-water flow is limited. Figure 3-21 shows that the thickness of the Wanapum Formation (based on the depth to the top of the Grande Ronde Formation) is less than 50 feet along the channel of the South Fork Palouse River in the reach from Pullman to Albion and along the channel of the North Fork for a considerable distance upstream from Colfax. The formation is less than 100 feet thick along many other stream channels in Washington.

3.3.4.2 Hydraulic Characteristics Barker (1979, page 29) describes the upper aquifer as follows. “Hydraulic conditions observed in wells above the primary aquifer system [lower aquifer] vary greatly from place to place, depending mainly on each well’s finished depth and on the number and nature of the water-bearing zones penetrated…

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“Well yield in the Pullman sub-basin are substantially less than those in the Moscow sub- basin. Typically yielding less than 20 gal/min, upper-aquifer wells in the Pullman sub- basin will not support heavy pumping. In contrast, upper-zone wells in Moscow have yielded sufficient water to satisfy the demand for university and public supply in that area until the early 1960s.” Barker’s description of the upper aquifer in the Pullman area likely applies to the western portion of the Palouse Basin. Hydraulic information on the upper aquifer is very limited outside of the Moscow area because most of the wells that penetrate this unit are used for domestic purposes.

3.3.4.3 Aquifer Boundaries The boundaries for the upper aquifer are similar to those described above for the lower aquifer. The upper aquifer likely extends through all of the bedrock gaps for the subareas but is discontinuous where stream valleys have cut partially or completely through the formation.

3.3.4.4 Horizontal and Vertical Hydraulic Gradients Construction of a water-level elevation map for the upper aquifer is difficult because of the downward vertical gradient that is present over much of the area. Barker (1979) created a map of presumed ground-water levels in the upper aquifer prior to development in the Pullman- Moscow subarea. His map, reproduced as Figure 3-28 shows westward ground-water flow with some apparent discharge into local streams.

3.3.4.5 Temporal Water-Level Changes Ground-water levels in the upper aquifer in the Moscow area have responded to operation of city production wells from the time of first development in the 1890s. Figure 3-26 shows that water- level decline was prevalent in the upper aquifer in Moscow until the 1960s when production wells were completed in the lower aquifer. Ground-water levels rebounded due to less pumping until pumping from upper aquifer production wells increased in the 1990s. Barker (1979, page 29) describes conditions within the upper aquifer outside of the immediate Moscow area. “Water levels in the upper aquifer zone in the Pullman sub-basin have characteristically declined less than 10 feet since first observed in the 1940s or 1950s… [T]he upper aquifers in most places have undergone little, if any, historical water-level decline.” Barker’s observations of the Pullman area, relative to water-level changes within the upper aquifer, appear to apply everywhere in the Palouse Basin except for the immediate Moscow area.

3.3.5 Ground-Water Flow Systems

3.3.5.1 General Flow System Theory Characterization of ground-water flow systems includes identification of the following components of the resource: 1) locations, sources, and mechanisms of ground-water recharge; 2) characteristics and controls for vertical and horizontal ground-water flow; and 3) locations and mechanisms of ground-water discharge. Ground-water recharge typically occurs at higher elevation locations within a basin where precipitation rates are higher and/or where losing surface water systems (streams or lakes) are present. Ground-water discharge typically occurs at

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Palouse Ground Water Basin Framework Project FINAL report lower elevation locations in a basin where hydrogeologic conditions prevent or limit further lateral ground-water flow. A component of the hydraulic gradient is downward in recharge areas because water is moving from surface recharge areas downward into the ground-water system. A component of the hydraulic gradient is upward in discharge areas because water is moving from deeper with the ground-water system to discharge locations at land surface. The dominant direction of ground-water flow typically is horizontal in the region between the recharge area and the discharge area. The direction of flow is from the recharge area to the discharge area. Geologic complexities in the subsurface result in a complex pattern of vertical and horizontal hydraulic gradients and ground-water movement.

3.3.5.2 Ground-Water Flow Systems in the Palouse Basin The Palouse Basin is located along the extreme eastern margin of the Columbia Plateau. Based on its topographic setting, the Palouse Basin is expected to be within the recharge area for the Columbia Plateau regional ground-water flow system. The logical discharge area from the regional ground-water flow system near the lowest portion of the basin is in south-central Washington. Based on this regional model, there should be a downward hydraulic gradient in the Palouse Basin, with generally horizontal ground-water flow out of the basin to the west- southwest. Hansen et al. (1994, pages 13-14) describes the regional flow system characteristics of the Columbia Plateau as follows. “Water-level data indicate that over most of the plateau the vertical component of flow is downward, except near discharge areas. Discharge areas generally are in topographic lows. Anomalies to this overall pattern are caused by geologic structures (some of uncertain nature), by ground-water pumpage, and by irrigation. “The potentiometric surface of the Saddle Mountains unit closely parallels the land surface in areas where little or no overburden is present, especially at higher altitudes. Ground water flows toward surface-drainage features. This pattern of flow is similar in the Wanapum and Grande Ronde where they are not overlain by another unit. Flow in the deeply buried parts of the Wanapum and Grande Ronde units is less controlled by surface-drainage features; water movement is controlled by vertical leakage… “Within the Palouse subprovince, north of the Snake River, ground water in both the Wanapum and Grande Ronde units flows toward the southwest, and regional discharge is to the Columbia and Snake Rivers. Here, water levels closely parallel the land surface and the regional dipslope of the basalts.” As is described above, there is a downward hydraulic gradient in the Pullman-Moscow subarea of the Palouse Basin between the loess and the upper aquifer and between the upper aquifer and the lower aquifer. This fits the regional flow-system model. However, the lower aquifer makes up most of the subsurface and there does not appear to be any detectable vertical or horizontal hydraulic gradient within the lower aquifer under current conditions within the Pullman-Moscow subarea. This suggests that the ground-water flow system in at least the Pullman-Moscow subarea is considerably more complex than can be described by the regional flow system model. The eastern portions of the Palouse Basin are located within ancestral valley(s) within the crystalline basement rocks and appear to be at least partially hydraulically isolated from the main body of the Columbia Plateau regional ground-water flow system. This is the case for the

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Pullman-Moscow subarea and may also be the case for the Northern subarea. The theory of partial hydraulic isolation pertains primarily to the lower aquifer. The upper aquifer is not laterally continuous in the western portion of the Pullman-Moscow subarea because canyons cut partially through the unit in several areas. The presence of a partial western boundary to the lower aquifer in the Pullman-Moscow subarea should have resulted in a local ground-water discharge area located east of the boundary with upward hydraulic gradients prior to development. The most logical area for the local ground- water discharge area would be in the vicinity of the South Fork of the Palouse River in the reach from Pullman to Albion.

3.4 Water Balance

3.4.1 Introduction An aquifer water balance comprises a comparison of recharge to discharge with the associated change of water in storage. Each quantifiable component provides key information, yet often there are many assumptions and many unknowns. A change in storage is the result of an imbalance in the recharge and discharge. Ground-water levels rise if recharge exceeds discharge. Conversely, the development of wells results in additional aquifer discharge and thus ground-water levels will fall if there is not sufficient recharge to offset this. An aquifer water balance has considerable uncertainty because of a lack of complete knowledge relative to recharge, discharge, and changes in storage. It is, therefore, necessary to continually add to the hydrogeologic knowledge, update the conceptual model, and refine these parameters. Prior to development, ground-water systems in the Palouse Basin were in a state of dynamic equilibrium. Natural recharge was equal to natural discharge, with water levels rising and falling in response to periods of higher and lower recharge rates. The withdrawal of water via wells results in a disequilibrium where the sum of well discharge and natural discharge exceeds recharge. This resulted in falling ground-water levels. If the pumpage rate is small and is held constant, the ground-water levels decline enough to either decrease the natural discharge rate or increase the natural recharge rate to balance out the well discharge. Ground-water levels then stabilize and the system is back in equilibrium. Ground-water discharge is always dependent on ground-water levels (head dependent). Ground-water recharge may or may not be head dependent. Ground-water levels will never stabilize if the pumping rates are allowed to increase each year. Knowledge of the hydrogeologic characteristics of the ground-water system under study is important in assessing the time needed to establish a new equilibrium if the pumping rate is held constant. These include the hydraulic properties of the aquifer, the locations of aquifer boundaries, the locations and characteristics of recharge areas and the locations and characteristics of discharge areas. Particularly important is the relationship between head changes and changes in discharge rate. The same characteristics are important if the recharge is head dependent. A continually increasing rate of well discharge necessarily results in a continuing rate of water-level decline. The purpose of this section of the report is to describe the pertinent literature related to the Palouse Basin ground-water balance. Three aspects of the Basin ground-water balance are addressed.

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 The loess-alluvium water balance includes an assessment of precipitation, infiltration from streams, runoff, evaporation from the soil, transpiration by plants, discharges in the form of seeps and springs, changes in soil-water storage, and downward water movement below the root zone which results in recharge to the upper aquifer.  The upper aquifer ground-water balance includes recharge from the overlying loess- alluvium and from streams, changes in aquifer storage, discharge to the overlying loess- alluvium and thus to springs or streams, ground-water outflow from the Basin, and downward leakage to the lower aquifer.  The lower aquifer ground-water balance includes recharge from the upper aquifer, changes in aquifer storage, discharge to the overlying upper aquifer, and ground-water outflow from the Basin. Surface sediment water balance results in estimates of recharge to and discharge from the loess- alluvium layer. The upper and lower aquifer water balances include vertical leakage. Thus, the water balances for each of the three layers are interconnected. Age dating of water from the upper aquifer and lower aquifer can provide insight relative to time of travel within these flow systems. The Barker (1979) numerical model represents the lower aquifer water balance. Lum et al. (1990) represents the water balance for all three layers and surface water gain/loss. The objectives of this section are to describe the:  Surface-water gain/loss;  Loess-alluvium water balance;  Upper aquifer water balance;  Lower aquifer water balance; and  Information provided by aquifer age dates. The water balance as represented in the numerical models is addressed in Section 3.5 of this report.

3.4.2 Surface Water Gain/Loss Streams can gain flow from ground water and can also lose water to ground-water systems. This can occur in different reaches and at different periods of time. Several approaches can be taken to stream gain/loss studies. First, flow measurements can be taken at stations along the stream and compared to determine either gain or loss. Second, stream water temperature can be used to locate gaining and/or losing reaches and can provide some measure of quantities involved. Third, ground-water levels, when compared to stream-state elevations, can be used to infer where streams should be gaining or losing but quantities cannot be determined. The streams of primary importance to the Palouse Basin are Paradise Creek, the South Fork of the Palouse River, Union Flat Creek, and the Palouse River. The surface-water/ground-water studies primarily involve the loess-alluvium because very few of the stream segments flow directly on basalt of the upper and lower aquifers. Additional analysis of the hydraulic connection of the upper and lower aquifers and surface water is presented in the Preliminary Data Gap Investigations Section 5). Sinclair et al. (2009) and Heinemann (1994) provide the most quantitative information relative to stream gain/loss for the Palouse Basin. Studies by Smoot and Ralston (1984) and Leek (2006)

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Palouse Ground Water Basin Framework Project FINAL report provide qualitative information on gain/loss conditions. Additional studies include Watershed Science (2006) and UI theses dealing with the UI Groundwater Field Laboratory. Sinclair et al. (2009) of WDOE examined the relationship between ground water and surface water for Paradise Creek, South Fork of the Palouse River, and the Palouse River in Washington. They conducted their study during low-flow conditions and examined water temperature, stream flow and stage, and water level data from in-stream piezometers and water levels from nearby wells. Figure 3-29a shows stream segments included in the WDOE study. Tables 3-2 and 3-3 provide surface-water discharge balances. Flux estimates of inflow and outflow are given for reaches of Paradise Creek and South Fork of the Palouse River in Figure 3-29b. Paradise Creek between the state line and Pullman is shown to be gaining. A major losing reach (reach #4) in the South Fork of the Palouse River exists immediately downstream of Paradise Creek and the South Fork within the city of Pullman. This loss may be important relative to surface-water/ ground-water interaction in the western portion of the Pullman-Moscow subarea. Figure 3-30 shows a map for reaches of the Palouse River. A similar graph of flux was not provided. The Palouse River had both gaining and losing reaches. Heinemann (1994) evaluated stream gain/loss in six Pullman-Moscow area streams that are incised in the basalt. He mentions that stream flow measurements collected by the USGS in 1984 suggest “a significant amount” of stream gain from the basalt and associated interbeds. He used geologic cross sections and stream temperature data to evaluate areas of stream gain. Heinemann found that stream gain occurs where the streams flow across the eastern margin of the Roza Member of the Wanapum Formation. This occurs along Union Flat Creek, the North Fork of the Palouse River, and Four Mile Creek (see Figure 3-31). The geology of this area consists of “relatively thick unconsolidated sedimentary deposits (clays, sands, and gravels) and semi-consolidated deposits (fractured shales)” (page 45). His conclusions are as follows (pages 47-48): “Significant [ground-water] discharge along streams are [sic] limited to the central portion of Union Flat Creek and the upper reach of the North Fork of the Palouse River. A lesser amount of ground water discharges along the lower reaches of Four Mile Creek and Paradise Creek. The South Fork of the Palouse River does not appear to be receiving significant ground water as the majority of near-stream wells have static water levels near or below stream elevations. “Specific conclusions: (1) Streams flow primarily on the Wanapum Formation. (2) The upper reach of the North Fork of the Palouse River and the central portion of Union Flat Creek receive significant ground-water discharge from aquifers within the Wanapum Formation. Four Mile Creek and Paradise Creek receive a lesser amount of ground water from the Wanapum Formation. (3) Sedimentary deposits of the Vantage unit, located along the eastern margin of the Roza flow, are a source of ground-water discharge to streams. These deposits accumulated during the hiatus between the Roza and Priest Rapid flows. (4) Seepage along the Snake Canyon walls is believed to be less than previously estimated, based on data obtained from the Copp well and from the static water level elevation contour map. Ground-water flow within the Grande Ronde Formation is believed to be toward the northwest away from the canyon. (5) A structural barrier controlling ground-water flow within the Grande Ronde Formation may exist south of Union Flat Creek near Wilcox. (6) The area west of Wilcox is believed to be a ground-water discharge area.”

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Of the concurrent surface water bodies studied, Heinemann (1994) and Sinclair et al. (2009) agree that Paradise Creek is gaining between Pullman and Moscow, and the South Fork of the Palouse is losing in certain reaches. Smoot and Ralston (1984) examined Union Flat Creek, Four Mile Creek, Paradise Creek, South Fork of the Palouse River, and Missouri Flat Creek for signs of stream loss and gain. They describe the reaches examined, the noted inputs and outputs, and the streambed material. The lower reaches of Four Mile Creek flow close to the Wanapum basalt. Missouri Flat Creek and Paradise Creek flow primarily on alluvium. The South Fork of the Palouse River flows over basalt just south of the intersection with Wilbur Creek. From there south along Evartsville Road the river noticeably loses water. Almost all of the creeks were noted to have basalt cobbles. Although no conclusions as to stream gain/loss areas were mentioned, the study was used to develop the numerical model by Lum et al. (1990). In describing the hydrogeology of the Pullman-Moscow subarea, Foxworthy and Washburn (1963, pages 19-20) state: “The upper artesian aquifers may discharge to the channel of the South Fork of the Palouse River, where the channel is lower than the general piezometric surface. However, within the Pullman sub-basin, the only reach of the South Fork that is lower than the piezometric surface is between Pullman and Albion. The deeper aquifers … and perhaps the lower of the two principal aquifers probably discharge to the canyon of the Snake River. “Natural discharge from the confined basalt aquifers [presumed to be from the lower aquifer] probably does not vary greatly from season to season. Seemingly, the only factors that could appreciably affect the discharge are fluctuations of the artesian head and perhaps fluctuations of the water table and stream levels in the area of discharge.” Hopster (2003) states that most streams and rivers in Whitman County including Union Flat Creek, South Fork of the Palouse River, and the Snake River have significant stream gain areas. She measured spring discharge during baseflow conditions along Union Flat Creek and the South Fork of the Palouse River and concluded that spring discharge was from the loess or the loess/Wanapum contact. However, she also concluded, based upon recession coefficients, that a majority of baseflow to Union Flat Creek, South Fork of the Palouse River, and Four Mile Creek is from the basalt (i.e. stream gain). Hopster’s review of the recession data suggests stream gain to the South Fork of the Palouse River whereas Heinemann’s review of water level data does not support significant groundwater discharge to the stream. Using their developed GIS database for recharge development, Murray et al. (2003) mention areas of stream gain and loss. Their analysis indicates stream loss accounts for only 16% of the ground-water recharge to the Basin and occurs primarily in the western area of the Basin because streams incise directly into the basalts. The eastern area of the Basin primarily has gaining streams. No additional field work was conducted. Li (1991), Pardo (1993), Kopp (1994), Optaz (2007), and Hernandez (2007) recognize that Paradise Creek loses water near the UI Groundwater Field Laboratory (previous called the UI Groundwater Research Site) based on water-level data from wells completed in the shallow sediments (sediments of Bovill) and the upper portion of the Wanapum Formation basalt flow. Opatz (2007) postulated a response in some of the deeper upper-aquifer wells as well as the

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Appaloosa Horse Club well to Paradise Creek in February 2006; however, the data were not provided. Investigators at the UI Groundwater Field Laboratory have shown that there is a downward hydraulic gradient within the basalt flow that is part of the Wanapum Formation (Li, 1991; Pardo, 1993; Kopp, 1994; and Hernandez, 2007). Ground-water levels are higher in wells completed opposite fracture zones in the middle of the basalt flow than in wells completed opposite the bottom portion of the basalt flow and underlying sediment. The investigators also determined that changes in streamflow are reflected in ground-water levels in the wells completed in the middle of the basalt flow but not in wells completed at the bottom of the basalt flow. Hernandez (2007) conducted aquifer tests at the UI Groundwater Field Laboratory near Paradise Creek; she also examined water levels and temperatures in upper aquifer wells. Her results indicate that seepage from Paradise Creek, South Fork of the Palouse River, and tributaries is the main source of recharge to the sediments of Bovill, mostly occurring February through May. The upper portion of the upper aquifer (upper portion of the Wanapum Formation basalt flow) is recharged by water migrating vertically from saturated sediments of Bovill into the fractured upper portion of the Priest Rapids Lolo Flow.

3.4.3 Surface Sediment Water Balance The surface sediment (loess and alluvium) water balance is important because the dominant source of recharge for the Palouse Basin is from infiltration of precipitation. The sediment water balance involves subtracting runoff from precipitation to get infiltration. The water that infiltrates can be evaporated or transpired by plants, or can go into soil moisture storage. Once soil moisture storage has been satisfied, water can move downward below the root zone and become recharge (deep percolation). Discharge from the surface sediment occurs as lateral flow to springs and seeps, to streams (see Section 3.4.2), and as downward flow to the upper aquifer. The surface sediment layer is found spatially almost universally in the Basin because few, if any, surface basalt exposures exist. It is, therefore, the primary “catchment” of all potential surface recharge. Much more is known about the surface sediment water balance than the water balance for either of the two basalt aquifers. The UI maintains a research site to investigate surface sediment water balance and shallow ground-water flow. This site is located outside the Basin in Troy, Idaho, but the mechanisms and processes are applicable to sediments inside the Basin because of the similar composition and deposition.

3.4.3.1 Ground-Water Recharge Besides recharge by stream loss, surface sediment recharge may be from either direct precipitation or lateral ground-water inflow from outside the Basin boundaries. The latter would include recharge from precipitation on highland areas and losses from streams on highland areas. 3.4.3.1.1 Recharge from Areal Precipitation The rate and distribution of ground-water recharge to the shallow sediments by infiltration are governed by several factors including:  Rates and forms of precipitation;  Evapotranspiration, including evaporation and transpiration by plants;

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 Runoff factors including topography;  Soil characteristics (e.g., vertical hydraulic conductivity, effective porosity, soil thickness);  Soil saturation (higher in winter and spring); and  Land cover (agricultural or urban areas). Ground-water recharge from precipitation within the boundaries of the Basin can be estimated by means of a water balance. Ground-water recharge is defined as the portion of precipitation that results in deep percolation (water that migrates below the root zone). It is dependant upon the amount of evapotranspiration (intercepted by vegetation, transpiration, and evaporation) and surface runoff (Bloomsburg, 1959). Estimates of recharge rates from the surface sediment water balance studies range from 0.12 inches per year to 12 inches per year (Table 3-4). Most rates are estimated for the water which migrates below the root zone. The large range in recharge rates is a result of variability in which the studies were conducted, locations of the studies, differences in professional judgment for estimated values, or human error. Based on the most recent data, the highest rates probably are not representative of field conditions. Water balance studies of the Columbia Plateau have yielded estimates of recharge from precipitation as part of the Regional Aquifer System Analysis (RASA) Program. Vaccaro and Bauer (1987) conducted a water balance study over 53 watersheds underlain by Columbia River Basalt in Washington, Idaho, and Oregon. Their study area included the Palouse Basin. They found deep percolation ranged from 0.0 to 16.7 inches per year for rangeland model cells. Based on modeling efforts, Bauer and Vaccaro (1990) calculated average ground-water recharge rates in or near the Palouse Basin (mostly the Pullman-Moscow subarea) to range from approximately 1 to 5 inches per year for predevelopment (1850s) and current (1980s multi-year composite) land-use conditions in their deep percolation model (see Figures 3-32 and 3-33, respectively). More specifically, the average recharge rate for the Pullman-Moscow subarea of the Palouse River Basin was determined to be 4.13 inches per year for predevelopment land-use conditions and 2.79 inches per year for current land-use conditions. The average recharge rate for the Union Flat Creek Basin was determined to be 2.98 inches per year for predevelopment land-use conditions and 3.65 inches per year for current land-use conditions with one year of fallow. The model was based on a 22-year average with variable weather, soil, and land uses. Over the entire Columbia Plateau, they calculated ground-water recharge rates to range from an average of 1.65 inches per year for predevelopment land-use (1850s) to 3.88 inches per year for current land-use (1980s multi-year composite). Updating the model, Vaccaro (1999) modified the Columbia Plateau recharge rates to 2.72 inches per year for predevelopment conditions and 4.24 inches per year for current conditions (Table 3-4). The hydrologic characteristics of the loess that covers the majority of the Basin is important relative to recharge from areal precipitation. Several studies focus on where and when recharge occurs to the loess.  O’Brien and Keller (1993) evaluated the nature of shallow unsaturated flow at two sites located near Pullman. They studied conditions within the top, mid, and low hill slope in the loess using environmental tritium. They found the net recharge to the upper slope and mid slope to be 1-5 centimeters per year. Large lateral flow prevented accurate recharge calculations from being made for sites at the toe of the slope.

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 In a follow-on study, O’Brien et al. (1996) used chloride mass balances in conjunction with the tritium analysis to evaluate recharge to the loess-covered hill. The chloride mass balance shows a greater variability and heterogeneity than tritium. It was discovered that recharge fluxes were 5 to 10 times greater at the mid and toe slope than at the top and comprise 0.6-6% of the mean annual precipitation. Upper, mid, and toe slope recharge flux rates are 0.3, 3, and 2 centimeters per year, respectively. They acknowledge that recharge flux rates based on chloride distributions are 2 to 10 times less than determined by other methods.  O’Geen et al. (2002) also evaluated chloride profiles in the loess at the UI site near Troy, Idaho. They discovered that the buried Eb soil horizon and buried paleofragipan horizons impede vertical flow.  In a shallow sediment study (6-meter depths) using chloride and oxygen-18, O’Geen et al. (2005) studied soil recharge at three sites located: 1) east outside the Basin, 2) northwest of Pullman, and 3) south between Moscow and Pullman (see Figure 3-34). They found that of the three sites evaluated, recharge to the shallow sediments was greatest in the central and western part of the Basin (upwards of 1.0 centimeter per year) because of the less developed soils and regolith and the homogeneous nature of the deep regolith (loose, heterogeneous materials). They found the east site (near Troy, Idaho) to have more developed and heterogeneous regolith. Valleys where there is deep regolith receive about 0.5 centimeters per year of recharge. Areas where the deep regolith is heterogeneous and with paleosol fragipans receive 0.06-0.3 centimeters per year of recharge. The authors conclude the valleys, which have “active hydrologic regimes,” have the greatest potential for recharge despite their smaller areal extent. Figure 3-35 shows the spatial distribution of recharge rates.  Brooks et al. (2006) describe how the extent and thickness of restrictive soil horizons affects the amount of impediment of vertical water movement.  Provant (1995) predicts more recharge is available to occur in the valleys because the loess is thinner and there is more water available. Researchers agree that most recharge occurs in the late fall through spring months to coincide with precipitation trends.  In a shallow sediment study near Troy, Idaho, Brooks et al. (2000) determined that 88% of spring precipitation that fell along a hillslope plot became subsurface lateral flow; evapotranspiration was low during the spring.  At the same site near Troy, modeling by McDaniel et al. (2008) showed that only 2% of the water leaves the catchment area as deep percolation and 1% as lateral flow when averaged over a four-year period. The difference from the previous study is because evapotranspiration is higher during other parts of the year.  Moravec et al. (2010) state that 67% of the precipitation for a year occurs in October through April, which is, therefore, when most of the ground-water recharge occurs. In an analysis of oxygen-18 and tritium, they discovered that ground-water discharge tends to occur in the summer months and ground-water recharge tends to occur in the winter months.

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Ross (1965) points out that the water balance studies which predict recharge may overestimate the amount of ground-water recharge and can have wide error margins. She believes Bloomsburg (1959) had the most accurate estimate of recharge at that time because the study was conducted within the Basin and not extrapolated from other areas. Barker (1979) points out that using the “difference method” to estimate the amount of runoff, evapotranspiration, or infiltration can supply large errors; for example, 1 inch over 164,000 acres equals 14,000 acre- feet of water. Ground-water recharge from precipitation was also assessed through monitoring ground-water levels in the shallow sediments. The following studies were conducted:  Williams and Allman (1969) determined through the examination of water levels in piezometers located in the loess that precipitation percolates through the loess and recharges ground water mostly in the late winter or spring. They also state that the amount of recharge is dependent upon the cultivation practices, the type of crop grown in fields, and the areas beneath root masses.  Provant (1995) measured water levels in private wells screened in the shallow sediments in the Pullman-Moscow area in August and again in January. He found rapid water-level responses to recharge events in wells located in the shallow sediments; wells that showed a response were near the crystalline/basalt contact, near a basalt outcrop, or in a stream drainage. He asserts that infiltration through the Palouse Formation and the sediments of Bovill is the primary source of recharge. However, Provant goes on to say that in the Moscow area these sediments are finer grained, which reduces the permeability. Murray et al. (2003) developed a GIS database for ground-water recharge assessment of the Palouse Basin. They collected data from five cores and utilized information from soil survey maps and surficial geology maps along with binary weighting and index overlay modeling methods to provide values to the soil map units dependent on the certain soil characteristics, which were then linked to Basin recharge mechanisms. They state, “recharge through loess is the most spatially extensive recharge mechanism, operating over 71% of the total study area” (page 759). 3.4.3.1.2 Ground-water Inflow Ground-water inflow from the edge of the Basin may be an important source of recharge for ground water in the Pullman-Moscow and Northern subareas. Most of the available information on this topic is for the Pullman-Moscow subarea. Two aspects of this potential water supply source are important. First, a number of investigators have concluded that shallow sediments near the margin of the basalt have higher hydraulic conductivity than sediments in place further out into the Basin. Second, water is likely available for movement into the Palouse Basin from precipitation on upland areas and stream loss to ground water prior to crossing the Basin boundary. There have been two main field studies conducted with the purpose of assessing the amount of inflow along the Basin margins.  Fairly et al. (2006) used geostatistical methods to determine the drilling locations for 47 core holes along the east side of the Pullman-Moscow subarea in order to investigate the likelihood of recharge at the granite/basalt contact. Figure 3-36 shows the coring locations. They hypothesized the Sediments of Bovill would provide a pathway for

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recharge to the basalt aquifers. However, they consistently discovered the presence of low-permeability, fine-grained sediments overlying the basalt, which would impede recharge to the upper and lower aquifers. Six boreholes provided information to determine the fractured nature of the basalt flow top to assess the likelihood of vertical recharge. The boreholes drilled in the South Fork of the Palouse drainage showed clay filling the basalt fractures; basalt in the Paradise Creek drainage was less fractured and/or had unfractured sandstone overlying. Fairly et al. (2006) conclude that water infiltrates into the shallow sediments and flows laterally along the granite/basalt contract rather than recharging the basalt; however, they acknowledge that farther west where the low permeable sediments pinch out the water may infiltrate into the basalt.  Golder Associates and HDR Engineering (2008) conducted a study to assess the feasibility of artificial recharge on the southern flanks of Kamiak Butte by examining the stratigraphy and thicknesses of the overburden at the granite/basalt contact. Activities consisted of field reconnaissance including digging test pits, conducting infiltration tests, and conducting ground-penetrating radar investigations. Sufficient amounts of clay were discovered that were believed to hamper ground-water recharge. Other studies that addressed ground-water inflow across the Basin boundaries from precipitation and stream loss from highland areas are described below.  Bloomsburg (1959) calculated the amount of deep percolation over four years in the Crumerine Creek and Gnat Creek watersheds on Moscow Mountain. He found that deep percolation (recharge) varied from 7.1% to 22.2% of precipitation for the first two years and 15.7% to 35.0% of precipitation over the last two years.  Cherry (1986) also calculated recharge as deep percolation in the Crumerine Creek watershed. Based on the years 1969–1973, an average of 20% of precipitation ends up as deep percolation. The month of May had the most recharge and October through March had the least, influenced mostly by snow.  In a similar study and area, Davis (1971) calculated deep percolation to be 16% of precipitation. One potential pathway for ground-water to enter the Basin from the highlands area is through permeable sediments of paleostream channels (Laney et al., 1923; Foxworthy and Washburn, 1963; Ross, 1965; Crosby and Chatters, 1965; Lin, 1967; Provant, 1995; Bush, 1996).  Lin (1967) postulates the presence of paleo stream channels in the sedimentary interflow zones on the eastern edge of the Basin based on examination of water levels, well logs, and tracer flow studies in streams. She hypothesized that these sediments are in contact with the more permeable, vesicular flow top of the Wanapum Formation basalt and anticipated that the Wanapum was recharged from baseflow of two reaches of Crumerine Creek.  Provant (1995) concludes the same ground-water flow pattern based on: 1) higher water levels in wells near the crystalline rock/basalt contact following a potential recharge event, and 2) higher conductivity sediments detected in well logs. He states, however, that recharge only occurs in areas where the high-conductivity sediments are present. The GIS database developed by Murray et al. (2003) predicts that recharge along the

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Basin margins through seepage via the fractures constitutes 13% of the recharge to the Basin (compared to 71% from the loess and 16% from stream loss).  Jones and Ross (1969) describe the high iron content in the upper artesian zone (Wanapum) as being derived from weathered basement sediments (clays) along the eastern margins of the Basin. Other studies along the crystalline rock/basalt contact have shown contrary evidence to high- permeability sediments and therefore conclude that recharge via this pathway is limited. These include the following.  Laney et al. (1923) recognized that discontinuous sedimentary layers and the amount of clay-bearing loess inhibit vertical flow at the crystalline rock / basalt contact.  Bloomsburg (1959) found that maps provided by the Soil Conservation Service showed fine-grained sediments at the base of the Palouse Range which were thought to inhibit recharge.  Foxworthy and Washburn (1963) found that along the contact zone the sediments are thin, have a low permeability, and are generally covered by loess. The importance of ground-water inflow across the Basin boundary is still an open issue. None of the studies to date have provided a definitive estimate of ground-water inflow.

3.4.3.2 Ground-water Discharge Natural ground-water discharge from the loess-alluvium can occur: 1) downward to the underlying geologic units, 2) to springs and seeps, and 3) to streams (described in Section 3.4.2). Nearly all researchers believe discharge from the shallow sediments is mostly by means of downward leakage to the upper aquifer (e.g., Foxworthy and Washburn, 1963). Additional information relative to discharge from the shallow sediments is given by Hopster (2003). She studied the locations of springs and seeps from 17 sites along Union Flat Creek and the South Fork of the Palouse River. She concludes that the springs are fed from perched water tables in the loess or at the loess/basalt contact and not from the basalt itself.

3.4.3.3 Change in Storage A change in aquifer storage is reflected by a change in aquifer water levels. Figure 3-26 shows water levels in the different aquifers including the loess-alluvium (Leek, 2006). Water levels in the loess remain fairly constant, varying mostly with the seasons. This means that recharge has been approximately equal to discharge within the loess-alluvium for a long time.

3.4.4 Upper Aquifer Water Balance The focus of the upper aquifer water balance discussion is on the Moscow portion of the Pullman-Moscow subarea. This is the only portion of the Palouse Basin where significant ground-water pumpage occurs from the upper aquifer. Small-yield domestic wells have been constructed in the upper aquifer throughout the remainder of the Basin, but have little impact on the resource. Also, investigations of the upper aquifer within the Palouse Basin are limited almost exclusively to the Pullman-Moscow subarea.

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3.4.4.1 Ground-Water Recharge Russell (1897) provides a view of the upper aquifer in the Moscow area essentially prior to development. He notes that several wells flowed at land surface in central Moscow when drilled in the early 1890s. This means that predevelopment recharge to the upper aquifer must have occurred at elevations higher than about 2,560 feet, the approximate land elevation of the flowing wells. These wells had ceased flowing by the time of Russell’s field study in 1896. By 1960, Jones and Ross (1972) state the water level near the downtown Moscow wells had declined to 120 feet below land surface. Recharge to the upper aquifer occurs as downward leakage from the loess and Sediments of Bovil; inflow from the margins of the Basin; and losses from streams via the loess, Sediments of Bovil, and alluvium. Most researchers agree that the dominant recharge mechanism is downward leakage from the loess. However, there are no direct ways to determine the amount of recharge that occurs to the upper aquifer via this mechanism. The upper aquifer is known to receive recharge as noted by rebounding water levels in the upper aquifer after the City of Moscow began pumping water from the lower aquifer in the early 1960s (Figure 3-26). The potential for recharge to the upper aquifer from streams via leakage through the loess and alluvium has been evaluated by a number of investigators. Several wells completed at the UI Groundwater Field Laboratory near the middle of the basalt flow that is included in the upper aquifer have been shown to respond to higher stream flow events. A water-level response to a flood event has not been found in any of the wells completed at the bottom of the basalt flow or in the underlying sediment (lower portion of the upper aquifer). This does not preclude recharge to the aquifer from streams, but does indicate that the hydraulic connection is not direct. For example, Hernandez (2007) presents stream stage measurements for Paradise Creek and water level elevations in the INEL-D well at the UI Groundwater Field Laboratory; peaks in stream stage did not correlate to peaks in ground-water levels. Hernandez analyzed ground-water temperature data and found very little to no seasonal temperature change in the INEL-D well and in other Wanapum basalt wells including the Moscow Cemetery well. However, Robischon (2010b) detected what appears to be a correlation between a high-stage event in the creek during the summer of 2009 and a peak in upper aquifer wells located near the bottom of the basalt flow. Several studies have evaluated recharge to the upper aquifer without regard to the recharge mechanism.  Jones and Ross (1972) describe the hydrogeology of the Moscow area. They examined recharge to the upper aquifer by: 1) analyzing pumpage and water level records from the city wells using a mathematical model (based on image wells assuming no recharge), and 2) studying long-term water level records in observation wells. The results of their analyses suggest that pumping was not in excess of recharge during the period 1896- 1960. They disagree with previous researchers at that time who determined recharge was in excess of discharge. Jones and Ross attribute the decline in water levels to barrier boundary effects and not a lack of recharge.  Baines (1992) developed an estimate of recharge (safe yield) for the upper aquifer based on analysis of average annual pumpage between two time periods when the water-level elevation was the same. His analysis is based on the presumption that the average pumping rate during a period of time when the water-level elevation is the same at the start as it is at the end is equal to the sustained yield of the aquifer. Figure 3-37 shows a

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plot of average yearly water-level decline in the USGS observation well completed in the upper aquifer in Moscow. The data plot may be divided into three different time frames: before 1964, during the period 1960-1969, and 1968-1986. These periods correlate to: pumping only Wanapum wells before 1964, a transitional period from high pumping to low pumping (1960-68), and when a lower level of pumping had been resumed in the upper aquifer (1968-86). Baines calculated the sustained yield for the upper aquifer to be 500-520 million gallons per year based on a water-level elevation of 2,479 feet in Moscow. This equates to a recharge rate of 0.70-0.73 inches per year based on a 41- square mile area. Baines notes that the calculated recharge rate of 0.8 inches per year using the Lum et al. (1990) data is about 50-70 million gallons greater than his sustained yield estimate. The sustained yield of the aquifer is higher if a lower water-level elevation is selected for analysis.  Provant (1995) measured water levels in wells in the Moscow-Pullman area in August and again in January. He found rapid water-level responses to recharge events in wells located in the Wanapum basalt in the eastern portion of the Basin; wells that showed a response were near the crystalline/basalt contact, near a basalt outcrop, or near a stream.  Bush (1996) states that recharge from precipitation through the loess and down to the basalt aquifers is not significant based on field observations during heavy runoff events and on the properties of the loess.

3.4.4.2 Ground-Water Discharge 3.4.4.2.1 Natural Discharge Natural ground-water discharge from the upper aquifer can occur as one or more of the following: 1) leakage to the lower aquifer, 2) springs and seeps via the loess-alluvium, 3) discharge to streams via the loess-alluvium, or 4) lateral flow out of the Basin. There is little doubt that discharge from the upper aquifer occurs to streams, springs, and seeps in the western portion of the Basin where drainages have cut down into the aquifer. Lateral outflow from the Basin to the west likely is limited because the aquifer has limited lateral continuity in this area. Downward leakage probably is the dominant natural discharge mechanism for the upper aquifer in the Moscow area. The discussion of discharge from the upper aquifer is very limited in the literature. Russell (1897) notes there are few springs in the basalt canyons during his visit, which was shortly after ground-water development was initiated. Golder (2005) states the locations of ground-water discharge are not well known. Baines (1992) examined the relationship of water levels (in the upper aquifer) to the postulated rate of leakage from the upper to the lower aquifers in the Moscow area. Rate of water-level decline in the upper aquifer in Moscow in the period from the 1940s into the 1960s was approximately the same as the rate of water-level decline in the lower aquifer as measured in Pullman during the same period (Figure 3-38). Thus the downward hydraulic gradient was nearly constant for this period. The downward gradient increased after the 1960s because of the water level recovery in the upper aquifer and the continued water level decline in the lower aquifer. Hopster (2003) examined recession curves from Union Flat Creek, South Fork of the Palouse River, and Four Mile Creek based on historical discharge data. Her interpretation is that the baseflow water is derived mostly from the basalt, probably the upper aquifer.

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3.4.4.2.2 Pumpage Most of the withdrawal from the upper aquifer has been and continues to be in the Moscow area. Prior to the 1960s, the water supply for UI and the city of Moscow was entirely derived from the upper aquifer. Currently, the City of Moscow operates two production wells completed in the upper aquifer, Moscow #2 and #3. UI also has several small-yield production wells. Most private well owners in the Basin have wells in this aquifer. Baines (1992) examined pumping records from wells in the upper aquifer in the Moscow area. Well pumping records from City of Moscow wells began in 1936 and continue through the present. Pumpage records for the UI wells are available from 1955 and are estimated prior to 1955 based on per capita data. UI upper aquifer wells were not pumped after 1964 due to sedimentation issues and are no longer used. Figure 3-39 shows the combined pumpage from these four wells for the period 1935-1990. There is a sharp decrease after 1964 when the City of Moscow and UI drilled their first wells in the Grande Ronde Formation. Moscow currently pumps 19-36% of its water from the upper aquifer (Robischon, 2010, personal communication, March).

3.4.4.3 Change in Storage A change in aquifer storage is reflected by a change in aquifer water levels. No studies were found that examined water levels in the upper aquifer outside the Pullman-Moscow subarea. Provant (1995) measured water levels in 53 private wells in August 1994 and in 20 of those wells again in January 1995 (see Figure 3-40 for well locations) within the Viola and Moscow West quadrangle to study the seasonal changes in ground-water levels. He found the change in water levels ranged from less than 1 foot to 18 feet in localized areas. Wells located in the eastern portion of the study area showed more of a response compared to those in the western study area (see Figure 4-41). He provides the following explanations (page 51): “Reasons for the rise in water level may be: 1) water use from private wells decreased from June, July, and August levels, allowing the aquifer to recover; 2) the upper aquifer is sensitive to seasonal fluctuations recharged through basalt exposures, stream loss or along paleostream-channel pathways; 3) recharge is being conducted through coarse- grained lenses within the sediments of Bovill to localized basins or permeable zones in the Priest Rapids basalt, where it can then infiltrate or 4) a combination of all three.” “The lack of water-level rises in the wells closer to Pullman might indicate that the deeper regional flow system is insensitive to seasonal fluctuations due to the longer pathway water must take to reach the Grande Ronde…” Provant (1995) also compared the measurements made in August 1994 to water levels collected in 1955, 1964, 1972, and 1975. Figure 3-42 shows wells with long-term water level decline. He found (page 47) that: “Measured private wells in the Wanapum aquifer [upper aquifer] show long term water- level declines of 0.11 to 16.18 feet, however long-term increases ranging from 4.03 to 58.8 feet were also recorded.” It is unknown whether the water-level response pattern documented by Provant represents aquifer conditions because a majority of the wells measured were in use.

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Barker (1979) states there has not been any long-term water-level decline in the wells completed in the upper aquifer outside of the Moscow area during the period studied. This would indicate that pumpage effects are small enough in the other parts of the Basin that equilibrium conditions have been established. Figure 3-26 shows water level elevations in the upper aquifer from 1923 to 2004 from Leek (2006); Figure 3-38 shows static water level elevations in the upper aquifer from 1935 to 2010. Water levels in the upper aquifer decreased until about 1964 before the City of Moscow and UI drilled their first wells in the lower aquifer and decreased (Moscow) or ceased (UI) pumping from the upper aquifer wells. Figure 3-43 is a graph that links upper aquifer water levels in Moscow #2 well and a USGS observation well to pumpage rates. Moscow well #2 is near the center of pumping and therefore has a greater variation. Both wells show the effect of terminating pumping from the upper aquifer in the 1960s and resumption of pumpage in the 1990s.

3.4.5 Lower Aquifer Water Balance There is great uncertainty in the amount of the Grande Ronde recharge and discharge because neither component of the water balance can be directly measured. Table 3-4 lists recharge values found in the literature for the Grande Ronde aquifer.

3.4.5.1 Ground-Water Recharge Very little is known about recharge to the lower aquifer. This is because of its great depth in some places and the fact that the water must migrate vertically through several geologic layers of varying thicknesses and vertical hydraulic conductivity before it even reaches the top of the aquifer. The dominant source of recharge is expected to be leakage from the upper aquifer. There may be additional recharge from stream loss where the stream channels are cut into the top of the Grande Ronde Formation in the western portion of the Basin. The rate of ground-water recharge as leakage to the lower aquifer is controlled by several factors:  Upper sediment characteristics;  Wanapum basalt and upper aquifer characteristics; and  Vantage Formation (sediments) characteristics. Leakage from the Wanapum basalt to the Grande Ronde basalt in most areas is through the Vantage sediments. The Vantage sediments are often included in the upper aquifer designation. Bush (1996) describes the Vantage Member clay-rich interbed between the Wanapum and Grande Ronde basalt formations as acting as an aquitard over much of Moscow, thereby reducing recharge to the lower aquifer. However, on the very eastern edge of the Basin this interbed is coarser and “vertical connection in places from the surface to the Vantage and on down to the lower units of the sediments of Moscow is likely” (Bush, 1996, page 4). The Vantage Member thins westward toward Pullman to a thickness of 2 feet, resulting in the likelihood of aquifer connection. These examples show there are at least two types of areas that could have potential for recharge to the lower aquifer. In two age-dating studies, Crosby and Chatters (1965) and Larson (1997) state that there is a limited hydraulic connection between the upper and lower aquifers. Despite the age dates,

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Palouse Ground Water Basin Framework Project FINAL report researchers believe leakage from the Wanapum basalt through the permeable zones of the Vantage Member supply recharge to the Grande Ronde basalt (e.g., Lum et al., 1990; Baines, 1992). It is also possible recharge could occur at locations where the Grande Ronde basalt is close to land surface and near a stream (see Figure 3-21). Douglas (2004) sampled 31 wells for a ground-water age-dating study (see Section 3.4.6 for more details of the study). She found a weak signature of increasing age with depth in lower aquifer wells (Figure 3-44). She provides the following explanation for limited recharge to this aquifer (pages 23-24): “Several potential factors, such as overburden thickness, fragipan development, thickness of the Wanapum Formation, and thickness of the Vantage Member, all collectively contribute to the restriction of vertical migration of infiltrating recharge water. These restricting factors are more prevalent in the eastern section of the Palouse Basin compared to the western section.”

3.4.5.2 Ground-Water Discharge 3.4.5.2.1 Natural Discharge Ground-water discharge from the lower aquifer in the Palouse Basin may occur from: 1) springs and seeps in those areas where canyons have been incised into the formation, 2) stream gains in those areas where the streams have been incised into the formation, and 3) ground-water outflow to the west. Discharge via springs, seeps, and stream gain along the South Fork of the Palouse River likely were important under predevelopment conditions. Present ground-water levels are below the valley floor in the river reach from Pullman to Albion (Sinclair et al., 1990).  Sokol (1966) states that before Moscow began pumping from the Grande Ronde, the natural discharge from all the aquifers was to the west.  Lum et al. (1990) and Brown (1991) assert that the lower aquifer discharges water as seeps in the Snake River canyon wall or directly into the river. However, it is now believed that ground water from the Pullman-Moscow subarea of the Palouse Basin does not discharge in significant quantities to the Snake River canyon because of the northwest trending structural fabric of the area. It is currently believed that any ground-water outflow to the west-northwest is the dominant discharge mechanism for the lower aquifer in the Palouse Basin. 3.4.5.2.2 Pumpage Pumping constitutes a significant portion of the discharge from the lower aquifer. All of the municipal water supply for the Palouse Basin, except for two Moscow wells, is from the lower aquifer. In addition, both universities use water from the lower aquifer. See Table 3-1 for a list of wells and associated information. Figure 3-45 shows the combined annual pumpage from the lower aquifer excluding Colfax, Palouse, and Garfield. Pumpage remained relatively stable from 1992 to 2003. The stabilization of pumping by Moscow, Pullman, UI, and WSU is a direct result of a water management agreement dating back to the early 1990s. After 2003, pumpage rates actually decreased over time to below the 1992 pumpage rates despite an increase in population.

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The change in storage due to pumping from the lower aquifer affects the natural recharge and discharge rates (Brown, 1991). As the water level declines, the amount of natural discharge decreases and the amount of recharge increases due to an increase in the downward vertical hydraulic gradient. Very little is known about the relationship between water-level decline and the associated changes in natural recharge and natural discharge for the lower aquifer.

3.4.5.3 Change in Storage A change in aquifer storage is measured by a change in aquifer water levels. Figures 3-26 and 3- 38 show that water levels in the lower aquifer have continued to decline over the period of record. Most researchers state that recharge is less than discharge in the lower aquifer. EBASCO (1958) states the USGS estimated recharge to be about half of pumpage. Crosby and Chatters (1965) estimated recharge to the Pullman sub-basin to be about 10% of the then-current pumpage rate. In their numerical model water balances for the lower aquifer, Barker (1979) and Lum et al. (1990) showed the sum of natural discharge and pumping discharge exceeded recharge, even though recharge exceeded pumpage. There is no analysis or figure found that correlates water level elevation and pumpage for the lower aquifer. Leek developed correlation graphs (not included in her 2006 thesis) from 1980 to approximately 1994. At best, a visual comparison can be made from Figures 3-45 from PBAC (2009) of the pumpage from the Grande Ronde aquifer (lower aquifer) in millions of gallons from 1992 to– 2008 and Figure 3-38 of historical water- level elevations. There appears to be a correlation between stabilized pumping rates and a decrease in the average rate of water-level decline in the lower aquifer.

3.4.6 Ground-Water Isotope Analysis The study of the time since water entered the ground provides insight into the characteristics of each of the two ground-water flow systems. Age-dating of water can be accomplished using three basic methods. Tritium and carbon-14, both radioactive, are frequently used for age-dating waters, whereas oxygen-18 and deuterium (combined as one method) are used to distinguish recharge areas (Freeze and Cherry, 1979). Fetter (1994) states that water following deep flow paths within an aquifer inherently has longer residence times than water at shallower depths. Longer flow paths are generally associated with slower flow velocity, and the water has further to travel. Therefore, older ages for deep ground- water flow systems are to be expected. Equating old ground water with limited aquifer recharge is not a valid assessment. Crosby and Chatters (1965) collected samples from 50 wells in the Basin to measure carbon-14 and/or tritium values. Only four of the samples were collected from the lower aquifer (Douglas, 2004): Pullman well #4, UI well #3, Moscow well #6, and Moscow well #8. Tritium values were used to verify the presence of young water. Crosby and Chatters found the water age and elevation of the production zone correlated well and that the water was well-stratified. The data could be categorized into shallow basalt water from Moscow, shallow basalt water from Pullman, and deeper basalt water. Based on their data table, waters from the basalt in Washington ranged from 3,180 years old to greater than or equal to 32,000 years old. Waters from the basalt in Idaho ranged from 7,340 years old to greater than or equal to 31,000 years old. They concluded that some recharge appears to have been occurring in the Pullman sub-basin but little to no recharge has taken place since the end of the Pleistocene glaciation time in the

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Moscow portion of the subarea. They found that water-level decline was slower in the Pullman sub-basin than in the Moscow sub-basin. They attribute this to a zone of impermeable clays and silts in the Moscow sub-basin inhibiting recharge to the deeper aquifer and a larger catchment area in the Pullman portion of the subarea as well as other geologic controls. They acknowledge their conclusions are based on limited data for the Moscow area. Recharge rates to the Pullman portion of the subarea were estimated to be 108 million gallons per year (331 acre-feet per year). Recharge in the Moscow portion of the subarea was assumed to be less. Silar (1969) conducted a follow-on study to Crosby and Chatters (1965) by sampling 44 wells with depths ranging from 63 feet below ground surface (bgs) to 300 feet bgs in basalt (implied but not stated) over the entire Columbia River basin; one well had a depth of 607 feet bgs. No wells were sampled in the Palouse Ground Water Basin. He used the same analysis methods as Crosby and Chatters. Silar found ages ranging from modern to 16,275 ± 1,465 years before present; modern age was the exception. Wells in the plateau areas contained relatively young water (less than 6,000 years before present). In the valleys, most of the water was 8,700 years before present to modern. He did not find a correlation between age and depth. Based on the aquifers studied, he concludes the morphology has a strong influence on the ground-water circulation, and the aquifers studied are not a part of the regional ground-water flow system based on the lack of zonality in ground-water ages. Larson (1997) used stable isotopic signatures of oxygen and hydrogen to assess aquifer recharge based on samples collected at different depths (shallow and deep) by comparing the ground- water results with the current precipitation ratios. For site locations see Figure 3-46. She concluded that the deeper basalt aquifer water is not the same water that is recharging the loess currently. The oxygen-18/oxygen-16 and deuterium/hydrogen ratios from ground water were compared to current precipitation values. Ratios from samples taken from the upper aquifer and upper portion of the lower aquifer in the Moscow area corresponded to Holocene precipitation values (i.e., less than about 10,000 years). The deeper lower-aquifer water ratios were lower than the current precipitation ratios. This indicates that the climate was cooler when the water was recharged. Larson concluded that precipitation that fell on the Basin has the same signatures as precipitation that fell on the Palouse Range, making it impossible to determine the spatial origin of the recharge. She could not determine if the recharge to the upper aquifer and upper portion of the lower aquifer is from precipitation or from streams. Larson did not find Holocene recharge to the lower aquifer in the Pullman portion of the subarea as Crosby and Chatters (1965) proposed. Based on her findings and those from Crosby and Chatters (1965), Larson concluded that the current estimates of recharge for the lower aquifer are too large. Douglas (2004) describes the relative ages from carbon-14 and oxygen-18 results for 31 ground- water samples collected from the wells completed in loess or granite plus the upper aquifer; an additional 23 samples were collected from wells completed in the lower aquifer. She states that the age dates are “model dates” and not exact dates due to the physical, chemical, and biological processes that affect carbon-14 values. The age dates show an approximate increase in age with depth in the lower aquifer (i.e. lower carbon-14 concentrations reflect older age dates) (see Figure 3-47). However, upper aquifer carbon-14 concentrations are highly variable at similar elevations. Douglas believes that this variability is caused by mixing of older with younger water within the upper aquifer. She also found that the oldest water at the pumping centers was in Moscow and Palouse, with youngest waters in the Pullman and Colfax areas (see Figure 3-48). The youngest water ages for the lower aquifer system were found around wells #30 and #29.

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This suggests potential recharge areas for the lower aquifer. Douglas calculated ages ranging from modern to 14,600 years in the upper aquifer, 4,400 to 11,800 years in the upper portion of the lower aquifer, and 13,000 to 26,400 years in the lower portion of the lower aquifer. The upper and lower sections of the lower aquifer are distinguished by a change in magnetic polarity. She sampled three of the same wells as Crosby and Chatters (1965). The age dates yielded comparable ages. Douglas states (page 19): “Because the ages fall into the same time period for each stratigraphic unit, it is apparent that the residence times for each unit have not been changed by 40 years of pumping in each of the major pumping centers. Ground water flow in horizontally layered Columbia River basalts occurs primarily within interflow zones between individual basalt flows, and wells completed in these interflow zones draw water radially from large horizontal distances. Water within specific interflow zones is expected to be similar in age because recharge water must traverse similar vertical travel distances.” Results from the oxygen-18 sample analysis compare with results from Larson (1997), showing oldest water in the lower aquifer, which is different from Holocene recharge (less than 10,000 years before present). Larson concludes the following (page 23). “Ground water in the lower [portion of the] Grande Ronde [lower aquifer] system is the oldest water in the basin, with a possible zone of recharge in the upper part of the Grande Ronde, occurring between the cities of Pullman and Moscow. Apparent stratification of ground water with similar 14C [carbon-14] age dates suggests that different ages reflect primarily vertical travel times from the land surface to the sampled locations.”

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3.5 Numerical Models

3.5.1 Introduction Construction and operation of a ground-water flow model necessarily requires synthesis and analysis of existing hydrogeologic data. This includes identification of model boundaries, estimation of necessary model inputs for which data are not available, calibration of the model within the constraints of uncertainty in model inputs, and operation of the model for predictive purposes. The following is a summary of the analytical and numerical ground-water modeling efforts that had a primary focus of the Palouse Basin.  Jones and Ross (1972) developed an analytical model of the upper aquifer in the Moscow portion of the Pullman-Moscow subarea. The model was based on the Theis equation and used image well theory to represent crystalline rock boundaries on the north, east, and south sides of the area. There was no western boundary to their modeled area. Jones and Ross used the model to evaluate whether pumping rates from the upper aquifer in the Moscow area could have resulted in the measured rate of water-level decline if there was no recharge. The measured rate of decline was much less than the model predicted in the absence of any recharge.  Barker (1979) constructed the first numerical model of the Palouse Basin. His single- layer model represents the lower aquifer in the Pullman-Moscow subarea with the western boundary of the model located along Union Flat Creek. He concludes that vertical leakage from the upper aquifer is the most important source of recharge. Natural discharge occurs as ground-water outflow from the basin and discharge to the South Fork of the Palouse River. Barker presents predictions of water-level decline rates under various pumping rate schemes.  Lum et al. (1990) constructed the second numerical model of the Palouse Basin with representation of an area somewhat larger than the present working boundary of the Basin (Figure 3-1). The modeled area includes the Snake River on the southwest, the city of Colfax on the northwest, and the city of Palouse on the northeast. The three layers of the Lum et al. model represent the loess, upper aquifer, and lower aquifer. The project included a water-balance study to estimate recharge rates and a surface geophysical study to gain a better understanding of the configuration of the crystalline basement rocks. Lum et al. present predictions of water-level decline rates under various pumping rate schemes.  Brown (1991) conducted a sensitivity analysis of the Lum et al. (1990) numerical model. The focus of his sensitivity analysis was on the areal recharge rate, the seepage discharge to the Snake River canyon, and the use of constant head versus constant flux to represent boundaries. He concludes that the Lum et al. model is insensitive to areal recharge rates.  Johnson et al. (1996) examined the representation of recharge to and discharge from the lower aquifer in the Lum et al. (1990) numerical model. They examine the potential use of a five-layer finite-difference model with three layers used to represent the lower aquifer. The five-layer model was not calibrated because of a lack of field data.

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The primary focus of this section of the report is on the representation of the aquifers within the Palouse Basin in the Barker (1979) and Lum et al. (1990) numerical models. The models are examined relative to five aspects: 1) model boundaries, 2) representation of the aquifers, 3) representation of recharge to the aquifers, 4) representation of discharge from the aquifers, and 5) predicted relationships of pumping to water-level decline. The contributions of Brown (1991) and Johnson et al. (1996) are also addressed.

3.5.2 Barker (1979) Model The Barker (1979) numerical model involved a finite-difference representation of the lower aquifer within the Pullman-Moscow subarea of the Palouse Basin. The model used a computer program developed by Pinder (1971) which is a predecessor of the USGS MODFLOW program currently in use. The Barker model was constructed as a single layer because of both computer limitations and the two-dimensional nature of the Pinder program. Barker (1979, page 58) lists the following as necessary model inputs.  Specified boundary conditions;  Transmissivity values for the primary aquifer system (lower aquifer);  Storage coefficient values for the primary aquifer system;  Pumping rates in wells tapping the primary aquifer system;  Thickness and hydraulic conductivity of the assumed confining layer between the upper aquifer zone and the primary aquifer system; and  Head distributions in both the upper aquifer and primary aquifer system.

3.5.2.1 Model Boundaries Barker (1979) selected an area that includes Pullman and Moscow for his numerical model (Figure 3-49). The contacts between the basalt and crystalline basement rock on the north, east, and south sides of the Pullman-Moscow area were represented as no-flow boundaries (Figure 3- 50). Barker used no-flow boundaries across the gaps between Kamiak Butte and Angel Butte and between Smoot Hill and Kamiak Butte, thus eliminating these potential aquifer extensions from further consideration. The no-flow boundary was extended west from Albion even though this area is underlain by basalt. The western boundary and a portion of the southern boundary of Barker’s numerical model were represented as constant-head areas. The western boundary is approximately aligned along Union Flat Creek. Barker (1979, page 59) provides the following justification for the modeling decision relative to Union Flat Creek. “Union Flat Creek was treated as a constant head boundary to the modeled aquifer system because: (1) the potentiometric surfaces of all explored aquifers immediately adjacent to the stream are apparently graded to and are hydraulically continuous with the stream, (2) the stream stage has apparently not changed, and is not expected to change, significantly with time, and (3) Union Flat Creek is hydraulically remote from the basin proper to a sufficient degree that reasonably small errors in the simulation for the stream area are not likely to significantly limit the accuracy or usefulness of simulated data for the basin study.”

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The logic for the constant head boundary along the western portion of the southern boundary is explained by Barker (1979, page 61) as follows. “The southern edge of the modeled area, between Union Flat Creek and the town of Chambers, was also treated as a constant-head boundary during model calibration. The rationale for this condition being used here is that the area south of the modeled area is virtually free of man-influenced changes in the natural environment, and the water levels are expected to remain essentially undisturbed by development in that area for at least 25 years. Because water levels in this area to the south are believed to be higher than anywhere else in the modeled area, flow across the boundary could be expected to increase in response to ground-water level development within the modeled area to the north.”

3.5.2.2 Representation of the Aquifers Barker’s single-layer numerical model represents the lower aquifer. Leakage from the upper aquifer to the lower aquifer is included in the model but the upper aquifer is not represented. The hydraulic properties of the lower aquifer are represented in terms of a calibrated transmissivity array (Figure 3-51). Transmissivity values, expressed as a range, were highest (0.3-0.325 square feet per second) in the center of the modeled area between Pullman and Moscow. Lower ranges of transmissivity are approximately concentric around the center of the model. The lowest range of transmissivity (0.001-0.009 square feet per second) occurs in a northwest-southeast trending band between Pullman and the western boundary of the model along Union Flat Creek. Barker uses this low transmissivity area to represent the “barrier zone” described previously. Barker considered storage characteristics under both confined and unconfined conditions. The confined storativity (storage coefficient) for the lower aquifer varies only a small amount across the model area. The western portion of the model area has a value of 0.005 transitioning to a value of 0.006 along the eastern edge of the model (Barker, 1979, page 66). Barker found that the storativity value had to be increased when the ground-water level dropped below 2,300 feet, which he described as the “top of the primary aquifer system” (Barker, 1979, page 68). Barker used a calibrated storativity value of 0.075 to represent unconfined conditions whenever the water-level elevation was below the top of the lower aquifer.

3.5.2.3 Representation of the Recharge to the Aquifers Most of the recharge to the lower aquifer in the model occurs as downward vertical leakage from the upper aquifer. This component was calculated in the model using the Darcy equation based on the vertical hydraulic conductivity of the confining layer between the two aquifers and the vertical hydraulic gradient, which is the head difference between the upper aquifer (an input value for each node) and the lower aquifer (calculated by the model) divided by the thickness of the confining layer between the two aquifers. A vertical hydraulic conductivity value of 2.0 x 10-9 feet per second was used for the model. Figure 3-52 shows that the confining layer thickness was greatest under Moscow and least under the South Fork of the Palouse River in the Pullman to Albion area. This means that leakage of water between the upper aquifer and the lower aquifer would be greatest in the Pullman to Albion area and lowest in the Moscow area. Additional recharge to the upper aquifer occurs as inflow from constant head nodes along the west end of the southern boundary and the upper portion of Union Flat Creek. Water entering

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Palouse Ground Water Basin Framework Project FINAL report the model along the west end of the southern boundary would represent ground-water inflow. Water entering from the southern end of the west boundary would represent ground-water gains or losses from Union Flat Creek.

3.5.2.4 Representation of Discharge from the Aquifer Discharge from the lower aquifer under predevelopment conditions is represented in the model in two ways. The first discharge pathway is upward leakage to the Wanapum Formation with presumed discharge into the South Fork of the Palouse River in the reach from Pullman to Albion. Secondly, discharge can occur via the constant head cells along the west side of the model. The discharge could represent either stream gain in Union Flat Creek or ground-water outflow to the west.

3.5.2.5 Predicted Relationship of Pumping to Water-Level Decline The model was calibrated using historical pumping records to match historical water-level data under both steady-state and transient conditions. Figure 3-53 shows a comparison of model- predicted water levels to the assumed predevelopment water levels from the steady-state calibration. The difference is less than 10 feet over most of the model area, with greater differences in a north-south band along the west side of the modeled area. Figure 3-54 shows a comparison of model predicted water levels in the lower aquifer to levels measured in 1974 and 1975. The measured ground-water elevations in Figure 3-55 show a comparison of model predicted temporal water levels to hydrographs of wells in Pullman and Moscow. The characteristics of the Barker’s calibrated model are shown via a sequence of figures.  Figure 3-56 shows simulated predevelopment water-level elevations with arrows showing predicted flux. Most of the Pullman-Moscow subarea had essentially the same water- level elevation. The steep hydraulic gradient along the west side of the modeled area reflects ground-water flow through the “barrier zone”. The flux numbers indicate that discharge from the eastern 80% of the modeled area was about 2,850 acre-feet per year. The only source for this water is downward leakage from the upper aquifer.  Figure 3-57 shows areas of predicted predevelopment vertical leakage reflecting water movement between the upper aquifer and the lower aquifer. Small amounts of leakage are shown along the eastern side of the subarea, reflecting the thick aquitard that separates the two aquifers. Areas of greater vertical leakage downward are shown on the western side of the subarea by the dark shading. Finally, an area of vertical leakage upward is shown aligned along the valley of the South Fork of the Palouse River and its tributaries in the general area of Pullman to Albion.  Figure 3-58 shows predicted 1975 water level elevations with arrows showing predicted flux. Water entering the model from the constant head nodes along the western side of the southern boundary is now important. Westward ground-water flow through the “barrier zone” has been decreased by more than 50%.  The 1975 map of predicted vertical leakage (Figure 3-59) shows downward leakage over more of the modeled area, with the lower leakage rate shown only along the eastern and northern portions of the subarea. The area of upward leakage along the South Fork of the Palouse River has been greatly reduced in size.

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 Figure 3-60 shows how the model predicts the impacts from the growth of ground-water withdrawals. The net vertical water movement from the upper aquifer to the lower aquifer has increased along with the induced recharge from southwestern portion of the model (south end of the barrier zone). Westward ground-water flow to the barrier zone has been reduced. Three figures show predicted relationships between future (relative to 1975) changes in pumping rates and changes in ground-water levels.  Figure 3-61 shows the simulated water-level decline if the average pumping rate for 1971-1975 (6,600 acre-feet per year) is held constant from 1975 to 2000. The model results show a reducing rate of water-level decline over the period, with about 9 feet of additional decline in the 25-year period. The model predicted that ground-water elevation in Moscow would consistently be about 4 feet lower than ground-water elevation in Pullman.  Figure 3-62 shows the simulated water-level elevation declines in 2000 if the 1971-1975 average pumping rate is doubled between 1976 and 1999. The decline during the 25-year period would be more than 20 feet over most of the modeled area, with more than 30 feet of decline in the Moscow area.  Figure 3-63 shows the simulated water-level elevations in 2000 if the 1971-1975 average pumping rate is tripled between 1976 and 1999. There would be more than 40 feet of water-level decline in the Pullman area and more than 50 feet of decline in the Moscow area.

3.5.2.6 Water-Budget Analysis Barker (1979) presents water budget information based on operation of his calibrated model of the lower aquifer. Table 3-5 presents Barker’s water budget for predevelopment conditions and 1975 conditions. Much of this information is shown on Figures 3-56 and 3-58. The following are important points taken from the water budget presentation.  The predicted water balance of the lower aquifer under predevelopment conditions included 5,225 acre-feet per year of recharge and discharge. About 79% of simulated recharge was downward leakage from the upper aquifer. Most of the simulated aquifer discharge was to the constant head boundaries, which represent both discharge to Union Flat Creek and ground-water outflow. A small amount of discharge is predicted to have occurred as upward vertical leakage into the upper aquifer and possibly the South Fork of the Palouse River.  The water budget is predicted to have changed considerably by 1975. The consumptive pumpage of 6,400 acre-feet per year is greater than the original recharge rate. According to the model, ground-water pumping has increased leakage from the upper aquifer of about 1,850 acre-feet per year. The remainder of the pumpage has been balanced by increased ground-water inflow from the south (1,700 acre-feet per year), decreased outflow out of the western boundary of the model (1,250 acre-feet per year), and decreased upward leakage (225 acre-feet per year). The final aspect of the 1975 water budget is the removal of 1,375 acre-feet per year from storage in the aquifer related to continual water-level decline.

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Table 3-6 presents water budgets by the year 2000 for three different pumping rates: 6,600 acre- feet per year, 13,200 acre-feet per year, and 18,600 acre-feet per year. Key points from the information presented in Table 3-6 are as follows.  A comparison of the 1975 conditions with a constant pumping rate of 6,400 acre-feet per year (Table 3-5) with the predicted year 2000 conditions with a constant pumping rate of 6,600 acre-feet per year (Table 3-6) shows relatively little change in the 25-year period. A decrease of water in storage would have occurred (275 acre-feet per year) with small changes in head-dependent inflow and outflow items (i.e., vertical leakage from the upper aquifer within the basin and barrier is predicted to increase from 5,975 acre-feet per year in 1975 to 6,100 acre-feet per year in 2000).  Doubling the pumping rate (relative to 1976) results in small changes in head-dependent recharge and discharge mechanisms but a large change in the amount of water removed from storage (Table 3-6). Tripling the pumping rate has the same general effect. As is shown on Figures 3-62 and 3-63, increased pumping is predicted to result in major, long- term water-level declines.

3.5.2.7 Recommendations Barker (1979) provides the following recommendations for future investigations.  A program of water-level monitoring should be continued.  Accurate and comprehensive pumpage data should be compiled on a continuing basis.  The storage coefficient should be considered for re-adjustment should the model not accurately predict the impacts of future pumping.  A better definition of the top of the primary aquifer system (lower aquifer) is another way to improve the model.  The “barrier zone” should receive intensive investigation.  Deepening and testing the WDOE test well would help in defining the Basin hydrology.  The use of surface water from within the Basin should be considered as an alternative to importation of water.  Moscow’s use of the upper aquifer should be increased.  Hydrogeologic investigations should occur throughout the Pullman-Moscow subarea and not just in one state or the other.

3.5.3 Lum et al. (1990) Model Lum et al. (1990) constructed a three-dimensional numerical model that was centered on the Pullman-Moscow area but covers a larger area than the model Barker (1979) constructed (Figure 3-64). The model layers represented the loess, the upper aquifer, and the lower aquifer (Figure 3-65). As part of the study, three cross-sectional flow models were constructed along estimated flow lines (northeast-southwest) in the lower aquifer to obtain hydraulic coefficients for input into the three-dimensional model. Two supporting investigations were also conducted. A separate modeling effort was used to develop estimates of recharge based on a soil-water

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3.5.3.1 Model Boundaries The boundary conditions for each of the three layers of the Lum et al. (1990) model are described below.  The loess model layer had no-flow boundaries on all sides. The eastern and southern boundaries represented topographic divides. Lum et al. (1990, page 29) indicated that the boundaries represented either topographic divides or canyons of the Snake River or the Palouse River.  The upper and lower aquifer model layers had the same combination of no-flow and constant-head boundaries (Figures 3-66, 3-67, and 3-68). o No-flow boundaries were used to represent the contacts with the crystalline basement rocks along the east side of the model. No-flow boundaries were also placed on the southwest side of the Snake River and the northern side of the Palouse River. Lum et al. (1990, page 29) justified the use of no-flow boundaries along the rivers as follows. “A horizontal no-flow (streamline) boundary beneath the Snake River is assumed because ground-water flow is upward to the Snake River… Boundary conditions similar to those for the Snake River are assumed for the Palouse River. The smaller size of the Palouse River suggests that it may not be a regional discharge area and that there may be underflow of ground water. Despite this uncertainty, however, the boundary is designated as no-flow … because it was thought to be sufficiently distant from the pumping centers of Moscow and Pullman that the effect of drawdown would be insignificant.” o Constant-head boundaries were used for three sections for both the upper and lower aquifer model layers (Figure 3-66). A constant-head boundary was placed along the southeastern boundary near the city of Colton. This constant-head boundary extended from the crystalline rock southwest to the Snake River. The second constant-head boundary had two components. The first segment extended north-south from the vicinity of the Snake River to the northwestern model boundary. The second segment then continued northeast along the model boundary to the intersection with the Palouse River. The third constant head boundary was along the northeastern edge of the model and connected the Palouse River to the crystalline rock outcrop. Lum et al. (1990, page 33) explain the use of constant head boundaries in these locations as follows. “A constant-head boundary creates a ground-water gradient into or out of the modeled area, depending on the hydraulic heads near the boundary. The model used this gradient to calculate a flux into or out of the appropriate geohydrologic unit at the location of the boundary.”

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3.5.3.2 Representation of the Aquifers Aquifer properties were determined through calibration of three cross-sectional models and then a time-averaged calibration of the three-layer basin model for the period 1974 to 1985. This period was selected because of the mass water-level measurements obtained by Barker in 1974 and Lum in 1985. Figure 3-69 shows the locations of the cross-sectional models and information for section B-B’, which extends from Moscow through Pullman to the Snake River. The hydraulic properties used in the Lum et al. (1990) model to represent the upper and lower aquifers include horizontal hydraulic conductivity and the ratio of horizontal to vertical hydraulic conductivity. The hydraulic properties in plan view for the two aquifers are shown on Figure 3-70. The hydraulic parameters for the upper aquifer are nearly uniform, with a slightly lower horizontal hydraulic conductivity in the northeastern portion of the modeled area than in the southwest portion. For the lower aquifer the horizontal hydraulic conductivity is highest in the northeastern portion of the Pullman-Moscow subarea, followed by the Pullman area. In the remainder of the model, values are at least one order of magnitude lower. The ratio of horizontal to vertical hydraulic conductivity is highest in the northeastern portion of the Pullman-Moscow area. Lum et al. (1990) do not provide a map of transmissivity values for the lower aquifer to allow a direct comparison with the Barker (1979) model (Figure 3-64). However, the Lum et al. (1990) hydraulic conductivity values multiplied by aquifer thickness estimates can be used to estimate transmissivity at several sites. The thickness of the Grande Ronde Formation varies from about 2,000 feet northeast of Pullman to about 1,000 feet overlying a crystalline rock knob located southwest of Pullman (see Figure 3-69). Figure 3-64 shows that the calibrated horizontal hydraulic conductivity is 12 feet per day near the deepest portion of the Basin and 5 feet per day over the bedrock high. Therefore, the calculated transmissivity value for the deepest portion of the Basin is about 24,000 square feet per day, with a transmissivity of about 5,000 square feet per day over the bedrock high. The transmissivity values used by Barker (1979) for the same approximate areas, converted to units of square feet per day, are about 26,000-28,000 square feet per day for the deepest portion of the Basin and about 8,600-16,000 square feet per day over the bedrock high. Thus, the hydraulic parameters used by Lum et al. (1990) and Barker (1979) are similar for the deepest part of the Basin. The Lum et al. (1990) value for the “barrier zone” located southwest of Pullman is somewhat lower than the value used by Barker (1979). Lum et al. (1990) used a final value of 0.001 for the storage coefficient for both the upper and lower aquifers. In contrast, Barker (1979) used a confined storage coefficient of 0.005-0.006 for the lower aquifer, with an unconfined storage coefficient value of 0.075.

3.5.3.3 Representation of Recharge to the Aquifers The dominant source of water entering the model is from precipitation entering the loess. The left side of Figure 3-66 shows the areal distribution of recharge to the loess layer under predevelopment conditions. The right side of the figure shows that the recharge is different under current conditions because of farming practices. The data presented on Figure 3-66 is the result of a soil-balance modeling effort conducted by the USGS for the general Columbia Plateau (Vacarro and Bauer, 1987).

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Recharge to the upper aquifer layer of the model is dominantly from downward leakage from the loess layer. Similarly, recharge to the lower aquifer is dominantly downward leakage from the upper aquifer. Some water enters the model from the constant-head boundaries located along the southeast (near Colton) and northeast (near the Palouse River) sides of the model. The amount of recharge to the upper and lower aquifer layers from the constant-head boundary nodes is head-dependent. Lowered ground-water levels near the boundary nodes within the Basin result in more water inflow.

3.5.3.4 Representation of Discharge from the Aquifers Water can discharge from the Lum et al. (1990) model in several ways. Water can discharge from the loess layer via nodes that represent interaction with streams and drain or constant-flux nodes that represent springs. The stream nodes are aligned along the drainage network in the Basin, and the drain and constant-flux nodes are primarily along the Snake River canyon. Drain nodes allow water-level changes to impact spring discharges while constant-flux nodes make the spring discharges independent of water-level changes. Stream, drain, and constant-flux nodes are also included in the upper aquifer layer of the model (Figure 3-67). Stream nodes are present along Paradise Creek, South Fork of the Palouse River, Palouse River, and the lower portion of Union Flat Creek. Drain and constant-flux nodes are mostly along the Snake River canyon. Water also can be discharged from the upper aquifer via constant-head boundary nodes along the northwestern boundary of the model and by pumping wells. Water can discharge from the model layer that represents the lower aquifer via constant-flux nodes that are located mostly along the Snake River canyon, via constant-head nodes located along the northwestern boundary of the model, and by pumping wells (Figure 3-68). In addition, the Snake River and Palouse River are simulated in the lower aquifer layer of the model.

3.5.3.5 Model Calibration The Lum et al. (1990, page 40) model was calibrated in a three-step process. “For this study, three cross-sectional models were calibrated independently to reproduce steady-state predevelopment conditions, and the three-dimensional model was calibrated to reproduce time-averaged conditions during 1974 – 1985. The three-dimensional model then was used to simulate historical drawdown in the area due to pumping during 1890 – 1985. This last step was intended to be a verification of the model, but much back-tracking, iterating from the cross-sectional to three-dimensional time-averaged to three-dimensional historical drawdown models, occurred. The calibrated models are a product of all of the available data sets…” The time-averaged calibration was based on the period from 1974 to 1985. These dates were selected because of the data collection programs of Barker in 1974 and Lum et al. in 1985. Lum et al. (1990, page 44) describe the time-averaged calibration process as follows. “Time averaging allows calibration of a three-dimensional model to recently collected data, which are commonly more complete than historical data… All transient conditions

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(changing water levels or pumping rates) are averaged over the same period so that they can be accounted for in what then becomes a steady-state simulation… A trial-and-error approach was used to calibrate the model. The goal was to simulate as closely as possible the observed average water levels for 1974 – 1985 and base flow in streams. The better-known input data for the model (thickness and extent of the geohydrologic units, recharge, and boundary conditions) were not altered during calibration. The input data least well known (hydraulic coefficients including horizontal and vertical hydraulic conductivity and the storage coefficient) were altered within a range that was considered reasonable on the basis of a literature search.” Model calibrated values of horizontal hydraulic conductivity and the ratio of horizontal to vertical hydraulic conductivity are shown in Figure 3-70 for the upper and lower aquifer layers of the model. Note that the calibrated horizontal hydraulic conductivity of the lower aquifer is higher in the Pullman-Moscow subarea than the lower aquifer in other parts of the model and the upper aquifer over the full extent of the model. A uniform value for the storage coefficient of 0.001 was used for both the upper and lower aquifer layers to represent the basalt units. The time-averaged calibration of the Lum et al. (1990) model resulted in a prediction of ground- water levels for the upper and lower aquifers for the time-averaged period of 1974 – 1985. Figure 3-71 shows both the model predicted values and the time-average measured heads at various well locations for both aquifers. The model-predicted ground-water levels indicate flow in the upper aquifer from east to west. The model results for the lower model layer indicate nearly uniform water levels in the Pullman-Moscow subarea, with a steep hydraulic gradient to the southwest in the area west of Pullman. The contours indicate model-predicted ground-water flow toward the Snake River. Operation of the model after completion of the time-averaged calibration resulted in a prediction of ground-water levels for the upper and lower aquifers through 1985. Figure 3-72 shows model-predicted water levels in UI well #3 (representing Moscow) and in WSU well #1 (representing Pullman). The temporal trends of the simulated data are similar to field measurement data. However, the predicted water levels in the Moscow well are much higher than field data; the predicted levels for the Pullman well are much lower than field data. Lum et al. (1990, page 52) explain the differences in simulated and field water-level data as follows. “Differences (as much as 10-30 feet) in absolute water-level altitude between simulated and observed hydrographs may result from limitations inherent in representing the Grande Ronde Basalt as a single model layer. Most wells in the area penetrated only the upper part of the Grande Ronde geohydrologic unit. Consequently, the water-level record for most wells is for the upper part of the formation, whereas simulated water levels represent the average over the model layer.” Figure 3-72 also shows a temporal comparison of predicted versus field data for the Pullman and Moscow wells. Simulated water levels are shown for projected 1% and 1.5% annual increases in ground-water pumping from the Pullman-Moscow subarea. Lum et al. (1990) indicate that the average increase in the pumping rate for the 1975 to 1985 period was about 1% per year.

3.5.3.6 Predicted Relationship of Pumping to Water-Level Decline The calibrated Lum et al. (1990) numerical model was used to predict future water levels under three different constant pumping scenarios and three scenarios where the pumping rate increases.

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The constant rate scenarios are: 1) at the 1981-1985 average rate, 2) 125% of the 1981-1985 average rate, and 3) 200% of the 1981-1985 average rate. Figure 3-73 shows these three scenarios as lines (a), (b), and (c), respectively, for both Pullman and Moscow. Ground-water levels are shown as drawdown from the 1985 levels. The model predicts that ground-water levels will trend toward equilibrium in all three constant pumping scenarios, with greater drawdown at the higher pumping rates. Inspection of the plots shows that ground-water levels should become approximately stable by the year 2005. The scenarios where the pumping rate increases represent the following conditions: 4) 0.5 percent annual increase, 5) 1% annual increase, and 6) 2% annual increase. Figure 3-73 shows these scenarios as lines (d), (e), and (f), respectively, for the wells in Pullman and Moscow. As is logical, the plots show a continual rate of water-level decline if the pumping rate continues to increase. Also as expected, the line for the 2% per year increase is steeper than the lines for the smaller rates of increase.

3.5.3.7 Water-Budget Analysis Lum et al. (1990) present a summary of the water budget for their numerical model after the time-averaged simulation. Their budget, presented in Table 3-7, shows the quantity of water in cubic feet per second that enters and leaves their model for the period of 1974 to 1985. Figure 3- 74 is a diagram that Johnson et al. (1996) prepared to show the water balance for the Lum et al. (1990) model. The figure shows that the recharge of 135 cubic feet per second (Table 3-7 shows 136 cubic feet per second) into the loess layer is predicted to result in downward flow of 59 cubic feet per second to the upper aquifer layer and 30 cubic feet per second of downward flow to the lower aquifer layer. About 75% of the discharge from the model occurs equally to the Snake River and seepage face, the drains (mostly along the Snake River canyon) and the rivers. The constant-head boundaries account for about 9% of the input to the model and about 13% of the output from the model. The recharge from and discharge to streams and rivers, as represented in the model, are detailed in Table 3-8. The negative values represent ground-water discharge to the surface-water systems. Measured discharge in selected streams is shown for low-flow conditions in October 1984. For example, the simulated average discharge into the South Fork of the Palouse River is 16.9 cubic feet per second and the measured low flow was 17 cubic feet per second. The simulated discharges into the smaller streams generally are greater than what was measured. The water balance for the lower aquifer, as represented in the Lum et al. (1990) model (Figure 3- 74), shows that downward leakage from the upper aquifer (30 cubic feet per second) plus inflow from the boundary (11 cubic feet per second) greatly exceeds the withdrawal via wells (9 cubic feet per second). Based on model operation, an increase in withdrawal rate would result in greater leakage from the upper aquifer layer, increased inflow from the boundary, and decreased outflow via the boundary, river, and canyon seeps.

3.5.3.8 Recommendation The Lum et al. (1990) report does not include a recommendations section. The single recommendation presented under specific conclusions is given below (page 63). “A program of continued data collection and model updating is needed for the area. Particular emphasis is needed on gaining a better understanding of locations and amounts of recharge and discharge.”

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3.5.4 Post Lum et al. (1990) Model Analysis

3.5.4.1 Brown (1991) Analysis Brown (1991) conducted sensitivity analysis on the Lum et al. (1990) model with respect to variations in: 1) areal recharge to the ground water Basin, 2) seepage discharge from the face of the Snake River canyon, and 3) constant-head versus constant-flux boundary conditions. Relative to changes in the recharge rate, Brown concludes the following. “Sensitivity studies demonstrate that simulated water levels in the Grande Ronde Basalt near Pullman and Moscow are relatively insensitive to changes in areal recharge, Snake River Canyon seepage, and model boundary conditions” (page vi). “Decreasing the amount of simulated areal recharge to the Pullman-Moscow model induces more drawdown to occur throughout the model in a projected simulation where municipal pumpage is increased by 1% annually… However, the water level changes are not proportional to the percentage adjustments in the recharge rate. In constant head boundary simulations when areal recharge is doubled or halved, drawdown in the Grande Ronde Basalt near Moscow and Pullman varies from the base simulation only by two to four feet at the end of 20 years of pumping… Significant changes in simulated areal recharge to the model only have a subtle affect on water levels in the Grande Ronde layer because the variation in recharge is accommodated mostly in the loess and Wanapum layers” (page 60). Brown (1991) recommends that the Grande Ronde Basalt (i.e. lower aquifer layer) be represented by several model layers. Also, the seepage face along the Snake River Canyon should be simulated with drains.

3.5.4.2 Johnson et al. (1996) Analysis Johnson et al. (1996) conducted an additional analysis of the Lum et al. (1990) numerical model as a follow-up to the Brown (1991) assessment. The greatest concern they had with the Lum et al. (1990) model is the uncertainty of recharge to and discharge from the deepest model layer, which represents the lower aquifer. Johnson et al. (1996) evaluated using three layers to represent the lower aquifer in an effort to improve representation of discharge to the Snake River. The five-layer model was not recalibrated because of inadequate information on aquifer water levels and characteristics.

3.5.5 Comparison of Field Data to Numerical Model Predictions

3.5.5.1 Summary of Barker (1979) Model Predictions The calibrated single-layer model constructed by Barker (1979) was used to predict future water levels in the lower aquifer under three different pumping rate scenarios. The conditions and the results of the modeling are described below.  The first model run represented holding the pumping rate constant at 6,600 acre-feet per year, which was the average of the annual pumping for the period 1971–1975. Water- level changes were simulated for a cell representing Pullman and a different cell representing Moscow. A temporal plot of water levels showed less than 10 feet of

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additional water-level decline in the period 1975 to 2000 with the rate of decline about 0.2 feet per year in 2000.  The second model run represented an annual increase in pumping of slightly less than 3%, starting with 6,600 acre-feet per year in 1975 and ending with about 13,200 acre-feet per year in 2000. The results of the simulation are presented in terms of total water-level decline for the period of 1975–2000. The predicted decline exceeded 30 feet for the 25- year period in both Pullman and Moscow.  The third model run represented an annual increase in pumping of about 4.6%, starting with 6,600 acre-feet per year in 1975 and ending with about 18,600 acre-feet per year in 2000. The predicted decline exceeded 55 feet in Moscow and exceeded 50 feet in Pullman for the 25-year period.

3.5.5.2 Summary of Lum et al. (1990) Model Predictions The calibrated three-layer model constructed by Lum et al. (1990) was used to predict future water-level changes in the lower aquifer with six different pumping rate scenarios. Lum et al. (1990, page 54) note that the growth in ground-water pumping in the lower aquifer in the Pullman-Moscow subarea was about 4.5% per year during the period 1891–1945, about 4% per year during 1946–1975, and about 1% per year from 1976 to 1985. The conditions and the results of the modeling are described below.  The first model run represented holding the pumping rate constant at about 7,500 acre- feet per year, which was the average of the annual pumpage for the period 1981–1985. The pumping rate was converted to acre-feet per year from the value of 6,700,000 gallons per day reported by Lum et al. (1990, page 54). Water levels are predicted for the period 1985–2005. Holding the pumping rate constant at about 7,500 acre-feet per year resulted in a decline of about 2.8 feet in the period 1985–2005. The predicted water levels in both Pullman and Moscow were approximately stable after about 15 years (about the year 2000).  The second model run represented pumping at a constant rate of 125% of the 1981–1985 average, or about 9,400 acre-feet per year. The predicted hydrograph shows rapid water level drop in the 1985–1990 period with the water levels approaching a stable value after about 20 years (about 2005). The total predicted water-level decline is about 25 feet in both Pullman and Moscow.  The third model run represented pumping at a constant rate of 200% of the 1981–1985 average, or about 15,000 acre-feet per year. Again, the predicted hydrograph shows rapid water-level drop in the 1985–1990 period with continued but decreasing water-level decline through the end of the simulated period in 2005. The total predicted water-level decline is about 92 feet in Pullman and about 99 feet in Moscow.  The next three model runs represent different rates of increase in the pumping rates from wells within the Pullman-Moscow subarea. The runs represent annual pumping rate increases of 0.5%, 1.0%, and 2.0%. As would be expected, the resulting hydrographs show continual rates of water-level decline. The predicted total water-level drops from 1985 to 2005 for Pullman and Moscow are given below. o 0.5% -- 11 feet in Pullman and Moscow

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o 1% -- 20 feet in Pullman and 21 feet in Moscow o 2% -- 41 feet in Pullman and 45 feet in Moscow

3.5.5.3 Summary of Historical Pumping Rates and Water-Level Decline Pumping information for the lower aquifer in the Pullman-Moscow subarea is available from annual reports of PBAC. The 1999 PBAC report provides a graph of combined pumping by Pullman, Moscow, UI, and WSU as a 5-year moving average starting in 1976. There was a steady increase in total pumping from about 6,900 acre-feet per year (2,250 million gallons per year) in 1976 to about 7,830 acre-feet per year (2,550 million gallons per year) in 1990. The 2008 PBAC report provides combined annual pumpage values from 1992 to 2008. The combined pumping rate remained relatively steady from 1992 to 2003, with a minimum value of 7,870 acre-feet per year (2,565 million gallons per year) in 1993 and a maximum of 8,140 acre- feet per year (2,652 million gallons per year) in 2003. The combined pumpage values have decreased from the 2003 value of 8,140 acre-feet per year to 7,460 acre-feet per year (2,431 million gallons per year) in 2008. The overall average pumping rate during the period of 1990 to 2008 is about 7,940 acre-feet per year (2,590 million gallons per year). As stated in Section 3.3.3.5, the hydrograph for the WSU test well (Figure 3-25) shows the following pattern of water-level decline in the lower aquifer in the Pullman area (Robischon, personal communication, 2010).  1935 to 1963 0.7 feet per year  1945 to 1961 1.45 feet per year  1965 to 1981 1.77 feet per year  1963 to 1985 1.7 feet per year  1985 to 1995 1.4 feet per year  1995 to 2007 0.86 feet per year

3.5.5.4 Comparison of Barker (1979) Numerical Model Predictions to Field Data The first Barker (1979) model run provides a prediction of water-level changes in the lower aquifer in the Pullman-Moscow subarea assuming a constant pumping rate of 6,600 acre-feet per year for the period of 1975 to 2000.  The model results predict a similar decreasing rate of water-level decline for wells in both Pullman and Moscow. The total predicted drawdown was about 8.8 feet in the 25-year period of 1975 to 2000. The predicted rates of water-level decline for different periods are given below (taken from the graph on page 96 of Barker, 1979). o 0.49 feet per year for1976 to 1984 o 0.33 feet per year for 1984 to 1992 o 0.23 feet per year for 1992 to 2000  The field data show that pumping rates have been approximately constant starting in 1990 at a rate of about 7,460 acre-feet per year. The actual average pumping rate is about 13 percent higher than assumed by Barker.

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 The rate of water-level decline predicted by Barker in the eight years after pumping was stabilized (1976–1984) of 0.5 feet per year is lower than the 1995 to 2007 field data rate of 0.86 feet per year. Both the model results and the field data show that the ground- water system has not come into equilibrium 20 years after stabilization of pumping. The second and third runs of the Barker (1979) model are not comparable to the field data since Barker assumed a continued annual increase in the pumping rate.

3.5.5.5 Comparison of Lum et al. (1990) Numerical Model Predictions to Field Data The first model run represents holding the pumping rate from the lower aquifer in the Pullman- Moscow subarea constant at about 7,500 acre-feet per year, which is the average of the pumping for the period 1981–1985. The pumping rate was converted to acre-feet per year from the value of 6,700,000 gallons per day reported by Lum et al. (1990, page 54). Water levels are predicted for the period of 1985–2005.  The model predicts a similar decreasing rate of water-level decline for wells in both Pullman and Moscow. The total predicted drawdown was about 2.9 feet in the 20-year period of 1985 to 2005. The predicted rates of water-level decline for different periods are given below (taken from the graph on page 55). o 0.33 feet per year for 1985 to 1991 o 0.15 feet per year for 1991 to 1999 o 0.01 feet per year for 1999 to 2005  The field data show that pumping rates have been held approximately constant starting in 1990 at a rate of about 7,460 acre-feet per year. The actual average pumping rate is approximately the same as used by Lum et al. (1990) in their model.  The rate of water-level decline predicted by Lum et al. (1990) in the six years after pumping was stabilized (1985–1991) of about 0.3 feet per year is much lower than the 1995 to 2007 field data rate of 0.86 feet per year. Additionally, the model predicted that the ground-water system would come into approximate equilibrium by about 2000. The field water-level data show that this has not occurred.

3.5.5.6 Discussion of Model Results Both the Barker (1979) and Lum et al. (1990) numerical models under-predict the long-term water-level decline in the Pullman-Moscow subarea. However, the Barker (1979) model is a better representation of the lower aquifer system than the Lum et al. (1990) model.  The Barker (1979) model predicts a long-term pattern of water-level decline with a decreasing rate of water-level change. The model results suggest that an equilibrium condition would be achieved decades into the future as long as pumping rates are held constant. The water-level pattern predicted by the Barker (1979) model is similar to what has occurred in the Basin with two exceptions. First, the rate of water-level decline predicted by Barker is smaller than what has occurred in the field, even adjusting for the differences in pumping rate. Second, the temporal reduction in the water-level decline rate is higher in the Barker (1979) model than has been measured in the field.

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 The Lum et al. (1990) model greatly under-predicts the current rate of decline and also reaches approximate equilibrium about 15 years after pumping rates are stabilized. The model predictions are a poor representation of what is occurring in the Basin.

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Chapter 3 Figures

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Northern Subarea Metamorphic or intrusive igneous rocks

Basalt and associated Western sediments Subarea

Pullman – Moscow Subarea

Approximate subarea boundary

Figure 3-1 Generalized geologic map of the Palouse Basin showing subareas (from Bush, 2005d).

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Figure 3-2 Map of area covered by the Columbia River basalts (from Hooper, 1982). Although difficult to distinguish, heavy lines represent the orientation, approximate position, and concentration of the feeder dikes. Hatched lines represent the anticlinal ridges.

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Figure 3-3 Stratigraphic units of the Columbia River Basalt Group in the Palouse Basin (from Bush, 2008).

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Figure 3-4 Altitude of the top of crystalline basement rocks (from Lum et al., 1990).

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Figure 3-5 Emplacement of R1 of the Grande Ronde basalt (from Bush, 2005d). P, M, and Pa represent Pullman, Moscow, and City of Palouse, respectively.

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Figure 3-6 Emplacement of N1 of the Grande Ronde basalt (from Bush, 2005d). P, M, C, and Pa represent Pullman, Moscow, Colfax, and City of Palouse, respectively.

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Figure 3-7 Emplacement of R2 of the Grande Ronde basalt (from Bush, 2005d). P, M, C, and Pa represent Pullman, Moscow, Colfax, and City of Palouse, respectively.

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Figure 3-8 Emplacement of N2 of the Grande Ronde basalt (from Bush, 2005d). P, M, C, and Pa represent Pullman, Moscow, Colfax, and City of Palouse, respectively.

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Figure 3-9 Emplacement of Roza Member of the Wanapum basalt (from Bush, 2005d).

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Figure 3-10 Emplacement of Priest Rapids Member of the Wanapum basalt (from Bush, 2006b).

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Figure 3-11a East-west geologic cross section (from Bush and Garwood, 2005f).

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Figure 3-11b East-west geologic cross section (from Bush and Garwood, 2005f).

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Figure 3-12 Panel diagram of the Palouse Basin (from Bush and Garwood, 2005h).

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Figure 3-13 Geologic cross section through IDWR (Moscow) Well #4 (from Bush, 2006a).

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Figure 3-14 Geologic cross section through Pullman Well #7 (from Bush et al., 2001a).

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Figure 3-15a Stratigraphy of the Pullman – Moscow area (from Conrey and Wolff, 2010).

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Elev (feet)

Figure 3-15b Stratigraphy and geologic cross section of the Pullman – Moscow area (from Conrey and Wolff, 2010).

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Figure 3-16 Locations of cross sections in the Northern and Western subareas (from Bush and Garwood, 2005f).

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Figure 3-17 Cross sections A-A’ and G-G’ in the Northern subarea (from Bush and Garwood, 2005f).

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Figure 3-18 Cross sections E-E’ and F-F’ in the Western subarea (from Bush and Garwood, 2005f).

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Figure 3-19 Cross section from Pullman to Colfax (from Leek, 2006).

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Figure 3-20a Preliminary structural contour map on the upper Grande Ronde surface; focus on Pullman – Moscow Subarea (from Bush and Garwood, 2005j).

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Figure 3-20b Preliminary structural contour map on the upper Grande Ronde surface (from Bush and Garwood, 2005j).

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Figure 3-21 Map showing depth to the top of the Grande Ronde Formation (from Robischon, 2010a).

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Figure 3-22a Location map showing production wells in the Palouse Basin.

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Figure 3-22b Well lithology and construction information on wells within the Pullman-Moscow subarea (from Fiedler, 2009).

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Figure 3-23 Water-level elevation data for the lower aquifer in the Pullman – Moscow subarea (from Barker, 1979).

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Figure 3-24 Plot of altitude of water level plotted versus altitude of the bottom of the well for wells in the Pullman – Moscow subarea (from Barker, 1979).

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Figure 3-25 Hydrograph for WSU test well (Robischon, personal communication, 2010).

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Figure 3-26 Hydrographs for wells completed in the loess, upper aquifer (Wanapum aquifer), and lower aquifer (Grande Ronde aquifer) in the Pullman – Moscow subarea (from Leek, 2006).

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Figure 3-27 Hydrographs for wells completed in the lower aquifer in Pullman and Palouse (from PBAC, 2001)

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Figure 3-28 Assumed water-level elevation map of the upper aquifer prior to development (from Barker, 1979).

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Figure 3-29a Map locations for springs, wells, streamflow gaging stations, and in-stream piezometers along the South Fork of the Palouse River and Paradise Creek (from Sinclair et al., 2009).

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Albion Pullman Colfax

Figure 3-29b Darcy flux estimates of potential streamflow gains and losses along Paradise Creek and the south Fork Palouse River, by seepage reach and river mile, for August 14-17, 2006 (from Sinclair et al., 2009).

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Figure 3-30 Map locations for springs, wells, streamflow gaging stations, and instream piezometers along the Palouse River (from Sinclair et al., 2009).

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Figure 3-31 Roza/Priest Rapids contact relative to ground-water discharge zones (from Heinemann, 1994).

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Figure 3-32 Estimated recharge distribution for predevelopment land-use conditions for the modeled zones imposed on the ground-water model grid system (from Bauer and Vaccaro, 1990).

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Figure 3-33 Estimated recharge distribution for current land-use conditions for the modeled zones imposed on the ground- water model grid system (from Bauer and Vaccaro, 1990).

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Figure 3-34 Digital elevation model of part of the Palouse Basin and its location in the Pacific Northwest (from O’Geen et al., 2005). Western, central, and eastern Basin study sites are indicated using the letters W, C, and E, respectively.

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Figure 3-35 Spatial representation of recharge rates for major hydrostratigraphic units identified from the SSURGO database (from O’Geen, 2005). Areas in white are regions without deep regolith. The letters P and M represent locations of Pullman and Moscow; western, central, and eastern study sites are indicated by W, C, and E, respectively.

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Figure 3-36 Location maps of core holes drilled for the Fairly et al. (2006) study. Circles represent shallow boreholes. Triangles represent deep boreholes.

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Figure 3-37 Plot of average yearly water level decline in USGS observation well versus average yearly pumpage from upper aquifer for 5 year moving periods, 1955-1987 (from Baines, 1992).

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Figure 3-38 Static water level elevations for the upper and lower aquifers (from Robischon, personal communication, 2010)

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Figure 3-39 Combined yearly pumpage from upper aquifer, Moscow and University of Idaho (from Baines, 1992).

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Figure 3-40 Locations for measured municipal and private wells in the Viola and Moscow West quadrangles (from Provant, 1995).

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Figure 3-41 Change in water-level between August 1994 and January 1995 for wells completed in the upper aquifer (from Provant, 1995).

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Figure 3-42 Long-term change in water-level between August 1994 and measurements conducted in 1955, 1964, 1972, and 1975 (from Provant, 1995).

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2520 700 2510 600 Moscow Wanapum 2500

500 1938 - 2009 GWMP 2490 400 Wanapum Annual Pumpage (MGY) Moscow # 2 St at ic (f t above MSL) 2480 USGS 300 2470 above MSL)

200 2460

100 2450 Wanapumannual pumpage (MGY) Wanapum level water elevation (ft 0 2 4 6 0 2 4 6 8 8 2440 6 8 0 7 8 8 8 0 2 4 7 7 7 9 9 2 4 6 8 6 6 7 9 9 9 4 6 8 6 8 0 5 6 6 6 9 9 9 1 1 1 8 0 2 0 2 4 5 5 5 9 9 9 1 1 1 0 2 4 6 0 0 0 8 4 4 5 9 9 9 9 1 1 1 8 9 0 0 4 4 4 9 9 9 1 1 1 9 9 9 9 0 0 0 3 9 9 9 1 1 1 1 8 9 0 0 9 9 9 1 1 1 9 9 9 9 2 2 2 9 1 1 1 9 1 1 2 2 1 1 1 1 1 1 1

Figure 3-43 Graph of upper aquifer (i.e. Wanapum) pumping rates and water level data in Moscow well #2 and the USGS well from 1938 to 2009 (from Robischon, personal communication, 2010).

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Figure 3-44 Isopach map of overburden thickness in the Palouse Basin showing lower aquifer sampling points (from Douglas, 2004). The Isopach map was modified after Hopster, 2003. The Isopach map likely has the color scheme reversed for overburden thickness based on the Hopster (2003) source.

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Figure 3-45 Discharge from the lower aquifer and the voluntary 1% annual increase target, 4 major entities combined (from PBAC, 2009c).

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Figure 3-46 Geographic distribution of 18O values in groundwater samples for the Larson (1997) analysis (from Larson, 1997). Groundwater samples from the lower aquifer are indicated by solid and open O’s. Samples taken from all other formations are represented by X’s. Open O’s indicate lower aquifer samples that fall out of the range of Holocene recharge. Closed O’s indicate samples that fall in the range of Holocene recharge.

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Figure 3-47 Arithmetic plot of 14C concentration versus elevation of the producing zone for ground water samples collected from the lower aquifer (Grande Ronde) and upper aquifer (Wanapum) systems (from Douglas, 2004).

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Figure 3-48 Shaded-cell map of ground water carbon-14 (pmc) concentrations in the lower aquifer system (from Douglas, 2004). Darker cells represent areas of younger waters.

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Figure 3-49 Location map for the Barker (1979) numerical model.

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Figure 3-50 Boundary identification map for the Barker (1979) numerical model.

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Figure 3-51 Calibrated transmissivity map for the Barker (1979) numerical model.

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Figure 3-52 Confining layer thickness map for the Barker (1979) numerical model.

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Figure 3-53 Differences between model predicted and assumed pre-development water levels for the Barker (1979) numerical model.

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Figure 3-54 Comparison of model predicted and measured water levels in 1975 for the Barker (1979) numerical model.

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Figure 3-55 Comparison of model predicted and measured water levels for selected wells for the Barker (1979) numerical model.

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Figure 3-56 Predevelopment water-level and water budget map for the Barker (1979) numerical model (flow in acre-feet per year).

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Figure 3-57 Model predicted pre-development vertical leakage map for the Barker (1979) numerical model.

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Figure 3-58 Model predicted 1975 water-level and water budget map for the Barker (1979) numerical model (flow in acre-feet per year).

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Figure 3-59 Model predicted 1975 vertical leakage map for the Barker (1979) numerical model.

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Figure 3-60 Model predicted recharge and discharge changes for the Barker (1979) numerical model.

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Figure 3-61 Model predicted water-level declines at the 1971-1975 average pumping rate of 6,600 acre-feet/year for selected wells for the Barker (1979) numerical model.

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Figure 3-62 Model predicted water-level declines in from 1975 to 2000 if the 1971-1975 average pumping rate is doubled between 1976 and 1999 for the Barker (1979) numerical model.

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Figure 3-63 Model predicted water-level declines in from 1975 to 2000 if the 1971-1975 average pumping rate is tripled between 1976-1999 for the Barker (1979) numerical model.

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Barker (1979) Model Lum et al. (1990) Model

Figure 3-64 Comparison of boundaries and hydraulic coefficients for the Barker (1979) and Lum et al. (1990) numerical models.

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Figure 3-65 Depiction of the model layers for the Lum et al. (1990) numerical model.

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Figure 3-66 Delineation of boundary conditions and areal distribution of recharge to the loess for predevelopment (left) and for current conditions (right) for the Lum et al. (1990) numerical model.

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Figure 3-67 Model grid and cell explanations for the upper aquifer (Wanapum) layer of the Lum et al. (1990) numerical model.

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Figure 3-68 Model grid and cell explanations for the lower aquifer (Grande Ronde) layer of the Lum et al. (1990) numerical model.

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Figure 3-69 Location and configuration of cross sectional models for the Lum et al. (1990) numerical model.

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Upper Aquifer Lower Aquifer

Figure 3-70 Horizontal hydraulic conductivity and the ratio of horizontal to vertical hydraulic conductivity for the Lum et al. (1990) numerical model.

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Upper Aquifer Lower Aquifer

Figure 3-71 Calibrated water-level elevations for the time averaged period of 1974 – 1985 for the Lum et al. (1990) numerical model.

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Figure 3-72 Comparison of observed and simulated water levels in wells for the Lum et al. (1990) numerical model.

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Figure 3-73 Simulated water levels in Pullman and Moscow from the Lum et al. (1990) numerical model. (a) the 1981-1985 average rate; (b) 125 percent of the 1981-85 average rate; and (c) 200 percent of the 1981-85 average rate; and at an annual pumpage rate increase from each preceeding year of: (d) ½ percent; (e) 1 percent; and (f) 2 percent; starting with the 1981-1985 average rate.

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Figure 3-74 Schematic of recharge and discharge to each layer of the Lum et al. (1990) numerical model (taken from Johnson et al., 1996).

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Chapter 3 Tables

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Table 3-1 Municipal and university well inventory (4 pages) Interval Screened/ Open to Open Elev. Specific Date Depth Aquifer Intervals (ft Capacity Owner Well No. Status Drilled Aquifer (ft) (ft bgs) (ft amsl) amsl) (gpm/ft) Reference(s) Comments/Discrepancies PBAC 1999 Annual Report, Golder 2 active 1925 WP 240 240 -- 2568 -- Associates 2005 PBAC 1999 Annual Report, Golder 3 active 1930 WP 569 240-569 -- 2569 -- Associates 2005 PBAC 1999 Annual 905- Report, Golder 6 active 1959 GR 1305 1305 -- 2586 -- Associates 2005 Golder Associates 7 -- 1978 GR 508 -- -- 2604 -- 2005 Moscow PBAC 1999 Annual Report, Golder Golder Associates 2005 has year 8 active 1965 GR 1458 1458 -- 2616 -- Associates 2005 as 1964, Elevation as 2618 feet PBAC 1999 Annual Report, Golder 9 active 1982 GR 1242 1242 -- 2557 -- Associates 2005 PBAC 1999 Annual cemetery inactive 1955 -- 508 456-508 -- 2604 -- Report Golder Associates 2007 has depth as 231, interval open to PBAC 1999 Annual aquifer (ft bgs) as 133-231, and abandon Report, Golder states it to be in WP and GR 2 00 1947 GR 213 154-213 2209-2111 2342 -- Associates 2007 aquifers Golder Associates 2007 has depth as 165, interval open to PBAC 1999 Annual aquifer (ft bgs) as 41-165, and Report, Golder states it to be in WP and GR 3 active 1947 GR 167 41-167 2299-2175 2340 10 Associates 2007 aquifers

Pullman PBAC 1999 Annual Golder Associates 2007 has Report, Golder depth as 954 and open interval 4 active 1957 GR 932 406-932 1936-1388 2342 3 Associates 2007 (ft bgs) as 406-954 PBAC 1999 Annual Report, Golder Golder Associates 2007 has 5 active 1969 GR 712 675-712 1773-1735 2447 33 Associates 2007 open interval (ft bgs) as 674-712

6 active 1968 GR 560 235-560 2189-1864 2424 4 PBAC 1999 Annual Report, Golder 160

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Table 3-1 Municipal and university well inventory (4 pages) Interval Screened/ Open to Open Elev. Specific Date Depth Aquifer Intervals (ft Capacity Owner Well No. Status Drilled Aquifer (ft) (ft bgs) (ft amsl) amsl) (gpm/ft) Reference(s) Comments/Discrepancies Associates 2007

Golder Associates 2007 has PBAC 1999 Annual elevation as 2342, depth as 718, Report Golder and open interval (ft bgs) as 276- 7 active 2001 GR -- -- 2066-1622 -- 473 Associates 2007 718 329-369, 2187-2144, 409-489, 2104-2024, 519-539, 1994-1974, 559-579, 1954-1934, 584-714, 1929-1799, Golder Associates 8 -- 2007 GR 793 754-794 1759-1719 2513 137 2007 PBAC 1999 Annual 890- Report, Golder 3 active 1963 GR 1337 1337 -- 2567 -- Associates 2005 PBAC 1999 Annual Report, Golder 4 active 1976 GR 747 687-747 -- 2552 -- Associates 2005 PBAC 1999 Annual aquacult 160-170; Report, Golder UI 5 ure 1991 WP 247 220-240 -- 2617 -- Associates 2005 PBAC 1999 Annual aquacult Report, Golder 6 ure 1993 WP 351 316-342 -- 2619 -- Associates 2005 PBAC 1999 Annual aquacult Report, Golder 7 ure 1993 WP 350 290-350 -- 2617 -- Associates 2005 PBAC 1999 Annual Report, Anderson et Anderson et al. 2008 says test monitor -- GR 144 144 2220 2364 -- al. 2008 Wanapum aquifer Rob Corcoran personal

WSU PBAC 1999 Annual communication (WSU Table) Report, Anderson et 2010 has status as inactive, well al. 2008, 2010 WSU depth as 223 feet, and drill date 1 active 1934 GR 247 247 2117 2364 12 Table as 1913

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Table 3-1 Municipal and university well inventory (4 pages) Interval Screened/ Open to Open Elev. Specific Date Depth Aquifer Intervals (ft Capacity Owner Well No. Status Drilled Aquifer (ft) (ft bgs) (ft amsl) amsl) (gpm/ft) Reference(s) Comments/Discrepancies Anderson et al. 2008 has no data listed for this well. Rob PBAC 1999 Annual Corcoran personal Report, Anderson et communication (WSU Table) al. 2008, 2010 WSU 2010 has status as abandoned, 2 monitor 1938 GR 214 214 -- 2358 -- Table and depth as 213 feet. Golder Associates 2007 has the open interval (ft bgs) listed as 200-223. Rob Corcoran personal PBAC 1999 Annual communication (WSU Table) Report, Anderson et 2010 has status as Inactive al 2008, 2010 WSU (broken shaft) and depth to be 3 active 1946 GR 223 158-213 2165-2142 2365 18 Table 247 feet Anderson et al. 2008 has the open interval (ft bgs) listed as 62-99, 203-272 and that it is in WP and GR aquifers. Rob PBAC 1999 Annual Corcoran personal Report, Anderson et communication (WSU Table) 2301-2264, al. 2008, 2010 WSU 2010 has status as emergency 4 active 1962 GR 275 165-275 2160-2091 2363 25 Table backup and year as 1963 Anderson et al. 2008 has the elevation as 2507 feet, and the open interval (ft bgs) as 300- 396. Rob Corcoran personal PBAC 1999 Annual communication (WSU Table) Report, Anderson et 2010 has status as emergency al. 2008, 2010 WSU backup, depth as 394 feet, and 5 stand-by 1963 GR 396 303-396 2207-1855 2505 9 Table year as 1964. Anderson et al. 2008 has the PBAC 1999 Annual open interval (ft bgs) as 396- Report, Anderson et 680. Rob Corcoran personal al. 2008, 2010 WSU communication (WSU Table) 6 active 1975 GR 702 340-702 2139-1855 2535 11 Table 2010 has year as 1973.

7 active 1987 GR 1814 ??-1814 1873-1836, 2416 270 PBAC 1999 Annual Anderson et al. 2008 has the 1743-1703, Report, Anderson et depth as 2224, the open intervals 1691-1641, al. 2008, 2010 WSU (ft bgs) as 543-580, 673-713,162 1508-1468, Table 725-775, 908-948, 1000-2224 Palouse Ground Water Basin Framework Project FINAL report

Table 3-1 Municipal and university well inventory (4 pages) Interval Screened/ Open to Open Elev. Specific Date Depth Aquifer Intervals (ft Capacity Owner Well No. Status Drilled Aquifer (ft) (ft bgs) (ft amsl) amsl) (gpm/ft) Reference(s) Comments/Discrepancies 1416-192

Rob Corcoran personal 8 active 2003 -- 814 -- -- 2587 -- 2010 WSU Table communication 2010 Fairview active 1955 GR 723 ------Well log Clay St. active -- GR ------Glenwood Well log (flowing

Colfax 1 -- 1915 GR 110 ------well) Glenwood Well log (flowing 2 -- 1927 GR 105.5 80-105.5 ------well) Town of Garfield and Walters and Glancy Walters and Glancy (1969) had 1 abandon 1908 GR 350 -- -- 2470 -- (1969) wells 1 and 2 reversed Town of Garfield and Walters and Glancy Walters and Glancy (1969) had 2 fire only 1909 GR 195 282-380 -- 2510 -- (1969) wells 1 and 2 reversed Garfield Garfield Washington Department of 3 active 1948 GR 380 ------Town of Garfield Ecology has year drilled 1912 4 active 1989 GR 315 -- 211-315 -- -- Town of Garfield 1889 or Robischon, personal #2 inactive 1890 GR ------comm.. 2010 PBAC 1999 Annual Report; Robischon, personal comm.., PBAC 1999 Annual Report; has Palouse Palouse old (#1?) active 1910 GR 297 220-297 -- 2433 -- 2010 the date drilled 1903 2000- PBAC 1999 Annual new (#3?) active 1999 GR 438 400-435 ------Report Notes: -- not available ft amsl - feet above mean sea level ft bgs - feet below ground surface (depth) GR – Grande Ronde (lower aquifer) WP – Wanapum (upper aquifer) Confusion as to well numbers for Palouse wells #1 and 2; Confusion as to well numbers for Garfield wells #1 and 2

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Table 3-2 Surface-water discharge balances for the South Fork Palouse River and Paradise Creek stream corridor (from Sinclair et al., 2009).

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Table 3-3 Surface-water discharge balances for the Palouse River (from Sinclair et al., 2009).

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Table 3-4 List of recharge values reported in the literature (2 pages) Different Recharge from Recharge Estimate previous Estimate (l/t) (l3/t) Area (l2) Reference Comments references 1,700 acre- 15,500 Laney et al. As deep percolation 1.32 in/yr * ft/yr acres (1923) from water balance. Packer (1955) (in Ross 1965 8,515 acre- 17,000 and Barker 6 in/yr * ft/yr acres 1979) Bloomsburg As deep percolation 2.3 - 12 in/yr (1959) from water balance. 4,000 acre- 40,000 Stevens 1.2 in/yr * ft/yr acres (1960) Through loess Grande Ronde - estimated using carbon Crosby and age dating. A) Moscow NegligibleA * 108million 250 square Chatters sub-basin; B) Pullman 0.5 in/yrB gal/yr miles (1965) sub-basin yes Determined by <0.68 - 1.36 numerical model. A) in/yrA * 4,900 acre- 88,000 Barker total recharge, B) Grande 0.67 in/yrB ft/yr acres (1979) Ronde recharge yes Cherry As deep percolation 7.5 in/yr 1570 acres (1986) from water balance. Determined by numerical model. A) 3.6 in/yrA Smoot total recharge, B) Grande 1 in/yrB 139 ft3/s (1987) Ronde recharge yes Columbia River Basin: Determined by deep percolation model based on a water balance. A) 32,000 Bauer and total recharge (current), 3.88 in/yrA 6,083 ft3/sA square Vaccaro B) total recharge (pre- 1.65 in/yrB 2,588 ft3/sB meters (1990) development) yes 750 square Determined by milesA numerical model. A) 2.8 in/yrA 150 square Lum et al. total recharge, B) Grande 2.0 in/yrB 136 ft3/s milesB (1990) Ronde recharge Johnson (1991) (in 4.13 in/year 2000 Larsen (10.5 cm/yr) square km 1997) Muniz (1991), in 0.98 - 4.06 in/yr 2000 Larsen (2.5 - 10.3 cm/yr) square km 1997)

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Table 3-4 List of recharge values reported in the literature (2 pages) Different Recharge from Recharge Estimate previous Estimate (l/t) (l3/t) Area (l2) Reference Comments references For the Wanapum aquifer and loess. Based on calculation using 570 million 41square Baines Lum et al. (1990) 0.8 in/yr gal/yr miles (1992) recharge rates Determined for loess 0.12 - 1.18 in/yr O'Brien et using chloride and (0.3 - 3 cm/yr) al. (1996) tritium signatures. yes Detailed information not provided. Columbia River Basin: A) total recharge (current), B) 4.24 in/yrA 10,205 ft3/sA Vaccaro total recharge (pre- 2.72 in/yrB 6,083 ft3/sB (1999) development)

0.012 to 0.24 O’Geen et Recharge to shallow in/yr al. (2005) sediment Note: *calculated for this report

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Table 3-5 Barker (1979) water budget information for pre-development and 1975 conditions.

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Table 3-6 Barker (1979) predictive water budget information for 1976 pumping rate and two different rates of pumping increase.

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Table 3-7 Lum et al. (1990) summary of water budget for time-averaged simulation.

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Table 3-8 Lum et al. (1990) simulated average flow into selected rivers and measured stream discharges.

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Section 4.0 Task 4.5 – Preliminary Data-Gap Investigation: Mass- Water Level Measurements

4.1 Introduction

Water levels were measured in a number of wells in the Palouse Basin in 1973-1974 and again in 1985 in support of numerical model studies (Barker, 1979 and Lum et al., 1990). Creation of a similar database in 2010 was identified as a data gap early in the Framework Project. Changing project scope allowed inclusion of a field water-level measurement program in a limited portion of the Palouse Basin in the ongoing project. In the mid 1970s, R.A. Barker, a USGS hydrogeologist, began to develop a numerical model of the Palouse Basin. In order to develop the model, a mass ground-water level measurement was conducted within the Palouse Basin during 1974. Lum et al. (1990) conducted a second mass water-level measurement in 1985 as part of the project to construct a second numerical model. In addition, the USGS has collected and recorded water-level measurements in selected wells for a number of years. Barker (1979) postulated the presence of a “barrier zone” or low hydraulic conductivity zone trending southeast-northwest in the area west of Pullman (Figure 4-1). Barker theorized that the rate of water-level decline in the lower aquifer would be considerably smaller within or west of the “barrier zone” than within the Pullman-Moscow area. The presence or absence of the “barrier zone” is very important in assessing the hydrogeologic boundaries of the Palouse Basin and potential water supply development alternatives. The purpose of this 2010 water-level measurement program is to use rates of water-level decline in wells to gain a greater understanding of the characteristics of the lower aquifer as it exists in the area west of Pullman. The steps involved in the water-level measurement sub-task are delineated below.

4.2 Selection of Study Area

The 2010 well measurement program was conducted in the west-southwest area of the Palouse Basin (Figure 4-2). Specifically, the area includes all of Township 15N Range 44E, Township 14N Range 44E, and parts of Township 15N Range 43E and Township 14N Range 43E.

4.3 Selection of Target Wells

A search was conducted on the USGS website entitled the National Water Information System, Groundwater Data for Washington (http://nwis.waterdata.usgs.gov/wa/nwis/gwlevels) to locate wells in the study area that have previous water-level measurements, particularly in 1974. Wells were initially searched using the lower aquifer criteria but not all wells had designated aquifers listed. The search included wells measured at least one other time, likely by Barker (1979) in 1973 or 1974 or Lum et al (1990) in 1984. Data fields provided by the USGS include:  Site name;  Township, range, section, quarter-quarter section;  Periods of record;

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 Number of previous measurements;  Hydrologic unit;  Latitude and longitude;  Elevation; and  Depth.

4.4 Review of List of Target Wells

The list of target wells was reviewed with the objective of ranking the sites relative to the criteria of completion of the wells within the lower aquifer and location in or near the “barrier zone” as identified by Barker (1979). Thirty-seven (37) wells were selected to be on the target list. Thirteen (13) wells were given a Phase 1 – high priority and 24 wells were given a Phase 2 – lower priority, with the priority based mostly on location. The wells were given priorities to assist in the measurement process focus. Table 4-1 lists the wells and associated information found from the USGS website or found in Barker (1979), including historical water-level measurements. Figure 4-2 shows the well locations. Where possible, well logs were obtained from the WDOE website or from the well owner. Few well logs were found (see Appendix B). Property ownership was determined by visiting the Whitman County Assessor’s Office in Colfax, Washington and accessing their files. In some cases it was difficult to determine the property owner because the target well is located in close proximity to the property boundary. Phone numbers were available for some owners. In certain cases the information provided was insufficient to find the property owner.

4.5 Field Measurement Project Plan

Field measurement of the well was attempted where the owner was contacted and permission was granted. Water levels in the wells were measured with a sonic water-level measurement device and/or an electric tape (e-tape). In all cases, the measurement device(s) used and any special circumstances were recorded in the field notebook and on the field sheets. Details of the field measurement program are included in the Quality Assurance Project Plan for the Palouse Ground Water Basin Framework Project, found in Appendix C. In some cases, well owners were not willing to have their well measured. Reported values for depth to water were collected if available. In one case, the well was measured creatively due to angled access piping. E-tape measurements provide the highest level of reliability because the water level is directly measured. Sonic water-level measurement device values were cross-checked with e-tape measurements and are believed to be reliable. Brief drawdown tests were conducted in some wells as a check on the accuracy of the sonic device measurements (see Appendix C). In certain instances where both measurement devices were used but provided differing values, the e-tape measurement was used. The sonic measurement device can be impacted by equipment within the borehole such as wiring. Both measurement approaches can be impacted by cascading water down a borehole.

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4.6 Field Results

Of the 37 wells selected to be measured, a total of 11 wells were measured by TerraGraphics although more wells were visited; TerraGraphics was provided the depth to water by the well owner for one well. Twenty-five (25) wells were not measured for a variety of reasons (Table 4- 2). For 10 wells, owners and/or contact information could not be found or owners did not want to participate. Owners could not be reached for five wells. Six wells were abandoned or were not found. One well was not measured due to unsafe conditions; one well cap was rusted on and the depth to water could not be measured. Data from two wells are not recorded based on other reasons. Table 4-3 lists the water-level measurement data for the wells that were measured in 2010. During the site visits it was discovered that new wells had been drilled; therefore, three additional wells were measured. These data are also included in Table 4-3. A discussion of each well measured is provided below.

4.6.1 Well 14N/44E-02M01 The period of water-level measurement record dates to 1950. The well depth is 93 feet below ground surface (bgs). No well log was found. This is a domestic well. Figure 4-3 is a graph of water-level elevations over the period of record. The water level has fluctuated over the period of record. The water level rose about 15.5 feet from 1950 to 1974. From 1974 to 2010 the water level fell about 2.5 feet.

4.6.2 Well 14N/44E-03P01 The period of water-level measurement record dates to 1954. The well depth is 176 feet bgs. No well log was found. This is a domestic well. Figure 4-3 is a graph of water-level elevations over the period of record. The water level rose 8 feet from 1954 to 1974, and then declined about 5 feet in the 37 years to 2010.

4.6.3 Well 14N/44E-05F01 This well was drilled in 1969. The period of water-level measurement record dates to 1974. The well depth is 242 feet bgs. The well log can be found in Appendix B. This is a domestic well. A concrete structure covers the well and requires special equipment to remove; TerraGraphics was therefore unable to obtain access to measure the depth to water. However, a depth to water measurement was provided by the owner based on a contractor measurement by TPM Water Systems. The measurement was determined by the water mark on the pipe when the pump was replaced. The contractor said the measurement is within 1-2 feet. The measurement date was August 5, 2009. Figure 4-4 is a graph of water-level elevations over the period of record for this well. The 2009 water level fits with the previous measurement. The water level declined 7 feet over 35 years; both water levels are significantly lower (more than 100 feet) than water levels in the other wells. This is one of the western-most wells that was measured.

4.6.4 Well 14N/44E-10B01 This well was drilled in 1966. The USGS has the well depth at 330 feet bgs, but the well log states a depth of 345 feet bgs. The well owner provided a well log (see Appendix B). The

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Palouse Ground Water Basin Framework Project FINAL report period of water-level measurement record dates to 1974. This is a domestic well. The owner stated that the well collapsed in the 1970s. Figure 4-3 is a graph of water-level elevations over the period of record. The 2010 water level is about 86 feet higher than in 1974. One reason for the water level rise is the well collapse as reported by the owner. Well 14N/44E-10B02 was drilled in 1974 as a replacement.

4.6.5 Well 14N/44E-10B02 This well was drilled in 1974. The well depth is 475 feet bgs. The well owner provided a well log (see Appendix B). The period of water-level measurement record dates to 1974. This is a domestic well. Figure 4-5 is a graph of water-level elevations over the period of record. Based on the two measurements, the water level declined 19 feet in the period 1974 to 2010.

4.6.6 Well 14N/44E-16P01 LE12 There is a fair amount of uncertainty regarding this well. In the USGS records, well 14N/44E- 16P01 LE12 has a reported depth of 60 feet bgs. In Barker (1979), well 14N/44E-16P01 has a reported depth of 140 feet bgs. The Barker-listed well was first measured in 1974 and the USGS-listed well was first measured in 1990. The property owner only knows of one well, although this was near a property boundary where other wells are located. The well owner stated the depth to water at some point was about 80 feet bgs then after his neighbor drilled a well the water level dropped to 200 feet bgs. The well was deepened in the early-mid 1990s. The depth to water in July 2010 was measured to be 28 feet bgs and the e-tape probe came up muddy, which is odd given the depths of these two wells. No well log was found. This is a domestic well. The USGS states well 14N/44E-16P01 LE12 is completed opposite basalt of the Saddle Mountains Formation. If the home owner is correct, the well measured is likely neither the well listed by the USGS nor the one listed by Barker. Therefore, a graph of water-level change is not provided for this location. The water level is described as a new well in Section 4.6.14.

4.6.7 Well 14N/44E-24J01 The period of water-level measurement record dates to 1951. The well depth is 162 feet bgs. No well log was found. This is a domestic well. Figure 4-3 is a graph of water-level elevations over the period of record. The water level has fluctuated over the period of record. The 2010 data indicate a water-level decline of 6 feet over 36 years.

4.6.8 Well 15N/44E-05A01 The period of water-level measurement record dates to 1915 and represents the oldest data for the wells measured in this study. The well depth is 120 feet bgs. No well log was found. This is a domestic well. Figure 4-3 is a graph of water-level elevations over the period of record. The water level has fluctuated over the period of record. From 1915 to 1974, the water level rose 37 feet. Then from 1974 to 2010, the water level fell 7.5 feet.

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4.6.9 Well 15N/44E-19B01 This well was drilled in 1939. The period of water-level measurement record dates to 1954. The well depth is 91 feet bgs. The USGS states this well is completed opposite basalt of the Saddle Mountains Formation. The information on the driller’s log is listed in Walters and Glancy (1969) and can be found in Appendix B of this report. This is a domestic well. Figure 4-3 is a graph of water-level elevations over the period of record. The water level has fluctuated over the period of record. Water levels decreased about 1.5 feet from March to October 1983. From 1983 to 1984 the water level rose about 5 feet and then dropped less than half a foot from 1984 to 1985. From 1985 to 2010, the water level rose 16 feet.

4.6.10 Well 15N/44E-21C01 The period of water-level measurement record dates to 1948. The well depth is 130 feet bgs. No well log was found. This is a domestic well. Figure 4-3 is a graph of water-level elevations over the period of record. The water level has fluctuated over the period of record. The most recent data indicate a water-level decline of 10 feet over the 36 years from 1974 to 2010.

4.6.11 Well 15N/44E-26L01 This well was drilled in 1950. The period of water-level measurement record dates to 1955. The well depth is 160 feet bgs. The information on the driller’s log is listed in Walters and Glancy (1969) and can be found in Appendix B of this report. The well was a domestic well that is no longer used. A new well has been drilled (see Section 4.6.14). Figure 4-5 is a graph of water-level elevations over the period of record. The water level continued to decline over the entire period of record at a fairly consistent rate of 71 feet in 55 years (1955-2010).

4.6.12 Well 15N/44E-33B01 This well was drilled in 1901. The period of water-level measurement record dates to 1944. The well depth is 175 feet bgs. The information on the driller’s log is listed in Walters and Glancy (1969) and can be found in Appendix B of this report. This is a domestic well. Figure 4-5 is a graph of water-level elevations over the period of record. The water level has steadily declined 70 feet in 66 years.

4.6.13 Well 15N/44E-35E01 This well was drilled in 1951. The well depth is 300 feet bgs; the USGS states this well is in the lower aquifer. A well log for this well is available in Appendix B. The period of water-level measurement record dates to 1954. Figure 4-5 is a graph of water-level elevations over the period of record. The water level in this well declined 38 feet from 1954 to at least 1975, but the 2010 measurement shows a rise of 47 feet. Because the surface pipe is at an incline, a garden hose was used to measure depth to water. The well is located in a field and was used for irrigation but is no longer in use. It is unknown why the water level rose for the 2010 measurement; likely, the well may have collapsed.

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The well owner stated that in 1953 the City of Pullman noticed that when this well was being pumped one of the artesian wells would “dry up”.

4.6.14 Additional wells measured An additional water-level measurement was taken during a site visit if another well was located on the property. This was the case for three wells. The fourth well was initially believed to be well 14N/44E-16P01 LE12 or 14N/44E-16P01, but the data do not indicate that the well visited was either of those wells. Figure 4-2 shows the locations of these wells. Table 4-3 lists the water-level measurement data. The four wells are: Small, Harlow, McKiernan, and Henson. Although GPS locations were collected for the new sites, ground elevations are not provided due to the inaccuracy of the instrument. Therefore, water-level elevations are not provided.

4.7 Discussion

There are many challenges to conducting a field ground water-level measurement program using private wells. Chief among the difficulties is ascertaining which well has historical measurements. Additional problems include changes in the well (such as collapse), well construction issues, measurement problems (cap rusted on), lack of contact information for well owners, and denied permission. WDOE had similar problems when they attempted such a program (Gregory, personal communication, 2010). All of the available data provided by the USGS and data acquired for this study are used in this discussion. Data from the 2010 USGS (Snyder and Haynes, 2010) report for the Pullman area are also utilized for comparison purposes; many of these measurements were provided by PBAC and not collected by USGS field personnel.

4.7.1 Bottom-Hole Elevation The likelihood of a well being in the lower aquifer was evaluated by comparing the bottom-hole elevations provided by the USGS for the 37 proposed wells to the Preliminary Structural Contour Map on the Upper Grande Ronde Surface constructed by Bush and Garwood (2005) (see Figure 4-6). Based on the contour map and the best estimate for well placement, 8 of the 37 wells had a bottom-hole elevation that was below the top of the Grande Ronde Formation (i.e., wells are screened within the Grande Ronde Formation) and thus likely represent the lower aquifer. Three of these wells were measured as part of this study. The following is a list of the eight wells:  15N/44E-35E01 (measured in 2010)  15N/44E-26L01 (measured in 2010)  14N/44E-10B02 (measured in 2010)  15N/44E-04A01  15N/44E-15G02  15N/44E-21D01  15N/44E-20D01

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 14N/44E-14P01 Using the same approach, the following wells measured in 2010 had a bottom-hole elevation that was in a formation above the top of the Grande Ronde Formation and thus likely represent the upper aquifer:  14N/44E-05F01  14N/44E-10B01  14N/44E-03P01  15N/44E-33B01  14N/44E-24J01  15N/44E-05A01  14N/44E-02M01  15N/44E-19B01 The following well measured in 2010 had a bottom-hole elevation that was close to the top of the Grande Ronde Formation:  15N/44E-21C01, about 35 feet higher than the top of the Grande Ronde Formation

4.7.2 Water-Level Elevation Versus Bottom-Hole Elevation A plot of water-level elevation versus well bottom elevation can help to better define the aquifer in which a well is screened. Figure 4-7 shows water-level elevation versus well bottom elevation for wells measured as part of this study in 2010 and also 2009 data from Pullman wells 3, 4, 5, 6, and 7, WSU wells 6 and 7, and the WSU test well (Snyder and Haynes, 2010). All of the 2009 data are from wells completed in the lower aquifer and had water-level elevations close to 2,242 feet above mean sea level (amsl). The wells measured in 2009 range widely in depth. This suggests that there is no vertical hydraulic gradient within the lower aquifer. Of the wells measured during this study only well, 15N/44E-26L01, plots near this elevation. Well 15N/44E-35E01, believed to have been constructed into the lower aquifer based on Figure 4-6, may have collapsed. This could explain the higher water-level elevation as compared to other lower aquifer wells. Well 14N/44E-10B02, believed to be in the lower aquifer based on Figure 4-6, has a water-level elevation about 50 feet higher than expected. It is possible that this well is not completed within the lower aquifer. It is also possible the well is located within or west of the Barker “barrier zone” and thus not significantly impacted by the cone of depression created by Pullman and WSU wells. All other wells measured with the exception of well 14N/44E-05F01 follow a pattern of water- level elevations that generally decrease with well depth. This suggests these wells may be located in the upper aquifer, which is supported by the data presented in Figure 4-6, or the wells may possibly be open to multiple aquifers. Well 14N/44E-05F01 has the lowest water elevation and the lowest bottom well elevation of the wells measured for this study. The water level measurement was not measured in 2010 but

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Palouse Ground Water Basin Framework Project FINAL report rather was determined by the company that pulled the pump based on the water mark on the pipe. The water-level measurement, if valid, raises a number of interesting questions. First, this could reflect a downward hydraulic gradient in the lower aquifer (if the well is located in the lower aquifer). However, well data from the City of Pullman and WSU suggest there is no vertical hydraulic gradient within the aquifer in the Pullman area. Second, well 14N/44E-05F01 could be completed in the Upper aquifer as indicated by the Bush and Garwood (2005) map. This could indicate an upward hydraulic gradient from the lower aquifer to the upper aquifer. Third, this well could also be located within or west of the Barker “barrier zone.”

4.7.3 Water-Level Elevation Versus Time Water-level elevation data are depicted in three different graphs based on water-level elevation. Wells with the highest water-level elevation data (2,300-2,600 feet amsl) are shown on Figure 4- 3. The graph shows a similar water-level fluctuation pattern with the exception of 15N/44E-19- B01 and 14N/44E-10B01, which show a water-level increase to the 2010 measurement. Most of these wells are believed to be located in the upper aquifer with the exception of possibly 14N/44E-10B01, in which the well likely collapsed. Well 14N/44E-05F01 has the lowest water- level elevation, as shown in Figure 4-4 on a scale from 2,100 to 2,300 feet amsl. It is difficult to draw any conclusions about this well based on water-level elevation data alone. Wells with the lower water-level elevation data (2,200-2,400 feet amsl) are graphed in Figure 4-5. These wells show similar rates of water-level decline with the exception of 15N/44E-35E01, but all are believed to be located in the lower aquifer. All three graphs (Figures 4-3, 4-4, and 4-5) have 200-foot y-axis scales. Figure 4-8 is a map showing the water-level elevation data measured in 2009 and/or 2010. Water-level elevations of the wells measured in 2010 range from 2,161 feet amsl in 14N/44E- 05F01 to 2,571 feet amsl in 14N/44E-24J01 (Table 4-4). Based on a spring 2009 water-level elevation of 2,242 feet amsl at the WSU test well (Snyder and Haynes, 2010), only well 15N/44E-26L01 has a water-level elevation that is “typical” of the lower aquifer. The other wells have higher water-level elevations by at least 50 feet except well 14N/44E-05F01. There also does not appear to be an areal pattern to the water-level elevations. Wells located very close to one another 14N/44E-10B02, 14N/44E-10B01, and 14N/44E-03P01 have water levels that vary from 2,307 feet amsl to 2,543 feet amsl (14N/44E-10B01 is the collapsed well). This can easily be explained by the wells being screened in different aquifers. Based on a similar water elevation to the Pullman and WSU wells, well 15N/44E-26L01 may be located in the lower aquifer in the Palouse Basin. Figure 4-9 is a graph of water-level elevations versus time for all of the wells measured in 2010 and includes all of the water-level data available. Table 4-4 lists all of the water-level elevations. Wells 14N/44E-03P01, 14N/44E-24J01, 14N/44E-02M01 have fairly high water-level elevations. Well 14N/44E-05F01 has the lowest elevation. Wells 15N/44E-26L01, 14N/44E- 10B02, and 15N/44E-33B01 have water-level decline patterns similar to the current lower aquifer water levels in the Palouse Basin, which has an average decline of 0.86 feet per year from 1995 to 2007 in the WSU test well. Wells 15N/44E-35E01 and 14N/44E-10B01 have a fairly substantial water-level rise of similar size from the 1970s to 2010. A water-level rise could be caused by a collapsed well. For wells with more than two data points, only wells 15N/44E-26L01 and 15N/44E-33B01 show a consistent water-level decline. Other wells with more than three data points have fluctuating water levels. This is consistent with water-level

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Palouse Ground Water Basin Framework Project FINAL report fluctuations found in wells located in the upper aquifer. Based on the water-level elevation patterns, wells 15N/44E-35E01, 14N/44E-10B01, 15N/44E-26L01, 14N/44E-10B02, and 15N/44E-33B01 may be located in the lower aquifer in the Palouse Basin.

4.7.4 Rates of Water-Level Decline Comparing rates of water-level decline for wells sampled in this study relative to rates of decline in the Pullman and WSU wells is another means of differentiating the penetrated aquifer. Table 4-4 provides all of the available water-level measurements, total drawdown from the first to last time periods, drawdown for each time period, and rates of water-level decline from the two most recent time periods. Water-level decline occurred in nine of the measured wells. Drawdown rates as determined from the 2010 data to the previous measurement data range from 0.07 feet per year in 14N/44E-02M01 to 1.1 feet per year in 15N/44E-26L01. Water-level rise occurred in three wells, 15N/44E-35E01, 14N/44E-10B01, and 15N/44E-19B01. Wells 15N/44E-35E01 and 14N/44E-10B01 are believed to have collapsed. Figure 4-10 is a map showing the water-level decline (or rise shown by negative values) in feet and the number of years represented. Figure 4- 11 is a map showing the rate of water-level decline (or rise as shown by negative numbers) since the previous measurement. Only wells 15N/44E-26L01 and 15N/44E-33B01 show a rate of water-level decline of approximately 1 foot per year. Well 14N/44E-10B02 shows only 0.5 feet per year of water-level decline. The average rate of water-level decline in the Pullman-Moscow portion of the Palouse Basin is 0.86 feet per year based on the WSU test well water level data from 1995 to 2007. The rates in wells 15N/44E-26L01, 14N/44E-10B02, and 15N/44E-33B01 suggest these wells are located in the lower aquifer in the Palouse Basin.

4.7.5 Comparison to the Barker (1979) Study Of the two wells measured in the current study and the Barker (1979) study, Barker concluded both wells 15N/44E-35E01 and 15N/44E-26L01 are located in the lower aquifer inside the Palouse Basin. Water-level data collected during the current study support his claim for well 15N/44E-26L01. The rise in water in well 15N/44E-35E01 likely is because of well collapse.

4.8 Conclusions

The focus of the effort was to obtain water-level measurements in selected wells that were measured in 1974 as part of the Barker (1979) aquifer investigation within the “barrier zone” in the lower aquifer. Field water-level measurements were obtained in 12 of the 37 wells selected for the effort. The remaining wells were not measured because of the following reasons: 1) the current well owner could not be located or would not give permission for the well to be measured; 2) the selected well could not be identified in the field, had been destroyed, or had collapsed; and 3) field conditions made it impossible to obtain a water-level measurement. The results of the field effort illustrate the difficulty of using old, private wells for a field investigation program. The water-level measurement program provides the following valuable information relative to the aquifers in the Pullman-Moscow subarea.

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 Data from wells 15N/44E-26L01 and 15N/44E-35E01 show that the lower aquifer with similar characteristics as in the Pullman-Moscow subarea extends west to a location along Highway 195 approximately midway between Pullman and Albion.  Well 15N/44E-33B01 is located about 2 miles west of wells 15N/44E-26L01 and 15N/44E-35E01 and has similar water-level elevations and a similar rate of water-level decline. However, well 33B01 appears to be too shallow to penetrate the Grande Ronde Formation as delineated by Bush and Garwood (2005). This well may be important relative to understanding the lower aquifer in the critical area west of Pullman and additional investigation in this area is warranted.  Well 14N/44E-10B02, located about 3 miles southwest of Pullman, has water-level characteristics that are slightly different from the lower aquifer in the Pullman-Moscow subarea. This well has a smaller rate of water-level decline and a higher water-level elevation than lower aquifer wells in Pullman. This well may be important relative to gaining a better understanding of Barker’s (1979) postulated “barrier zone” and additional investigation in this area is warranted.  All other wells measured are judged to be in the upper aquifer based on the following indicators: 1) bottom hole elevations above the top of the Grande Ronde Formation from the Bush and Garwood (2005) structural contour map; 2) higher water-level elevations that decrease with well depth (except in well 14N/44E-05F01) (downward vertical hydraulic gradient); 3) higher water-level elevations than in the Pullman and WSU wells (except in well 14N/44E-05F01); and 4) differing rates of water-level decline (or rise) in comparison to the Pullman and WSU wells.

4.9 Recommendations

The following are recommendations as a result of this study:  Put forth a greater effort into finding well owners and acquiring permission to measure water levels in the five unmeasured targeted wells that may be completed in the lower aquifer.  To the extent possible, gain additional information on wells 15N/44E-26L01, 15N/44E- 35E01, 15N/44E-33B01, and 14N/44E-10B02. This includes installing access tubes, if needed, and data loggers. Information from the data loggers would be used to identify possible water-level responses to differing pumping patterns from WSU and Pullman wells.

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Chapter 4 Figures

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Figure 4-1 Barrier zone as postulated by Barker (1979).

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Figure 4-2 Wells targeted for water-level measurement program in summer 2010.

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2600 2450

2550 2400

2500 2350

2450 2300

2400 2250 Water wells) top 3 listed (for (ft amsl) elevation level 1910 1920 1930 1940 1950 1960 1970 1980 1990 2000 2010 2020 Water botom (ft wells) (for 4 listed amsl) elevation level

14N/44E-03P01 14N/44E-24J01 Left-handed y-axis 14N/44E-02M01 14N/44E-10B01 15N/44E-21C01 15N/44E-05A01 Right-handed y-axis 15N/44E-19B01

Figure 4-3 Graph of water-level elevations for the period of record in wells believed to be located in the upper aquifer. Well 14N/44E-10B01 may be in the lower aquifer.

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2300

14N/44E-05F01

2250

2200

2150 Water data (ft amsl) elevation level

2100 1910 1920 1930 1940 1950 1960 1970 1980 1990 2000 2010 2020

Figure 4-4 Graph of water-level elevations for the period of record in well 14N/44E-05F01. Well is believed to be located in the lower aquifer but the scale is far below other upper aquifer wells. Elevation scale is still 200 feet.

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2400

2380

2360

2340

2320

2300

2280

2260 15N/44E-35E01 15N/44E-26L01

Water (ft elevation amsl) level 2240 14N/44E-10B02 15N/44E-33B01 2220

2200 1940 1950 1960 1970 1980 1990 2000 2010 2020

Figure 4-5 Graph of water-level elevations for the period of record in wells believed to be located in the lower aquifer.

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Figure 4-6 Bottom-hole elevations for all proposed wells overlain on the Bush and Garwood (2005j) structural contour map of the top of the Grande Ronde Formation.

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2600 15N/44E-35E01 14N/44E-05F01 2550 15N/44E-26L01 14N/44E-10B02 2500 14N/44E-10B01 14N/44E-03P01 2450 15N/44E-33B01 14N/44E-24J01 2400 15N/44E-21C01 15N/44E-05A01 2350 14N/44E-02M01 15N/44E-19B01 2300 Pullman 3 Pullman 4 2250 Pullman 5 Pullman 6

Water level elevation (ft amsl) (ft Water elevation level 2200 Pullman 7 WSU 6 2150 WSU 7 WSU Test 2100 0 500 1000 1500 2000 2500 3000 Well bottom elevation (ft amsl) Figure 4-7 Graph of water-level elevation (measured in 2009 or 2010) versus bottom-hole elevation.

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Figure 4-8 Map of water-elevation data collected in 2009 found in Synder and Haynes (2010) and 2010 for this program.

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2600

2550

2500 15N/44E-35E01 14N/44E-05F01 2450 15N/44E-26L01 14N/44E-10B02 14N/44E-10B01 2400 14N/44E-03P01 15N/44E-33B01 2350 14N/44E-24J01 15N/44E-21C01 2300 15N/44E-05A01 14N/44E-02M01 15N/44E-19B01 2250

2200 Water Level Elevation (ft amsl)

2150

2100 1940 1950 1960 1970 1980 1990 2000 2010

Figure 4-9 Graph of water-level elevation versus time.

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Figure 4-10 Map of feet of water-level decline per number of years based on range of water-level measurements, most recently in 2010.

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Figure 4-11 Map of rate of water-level decline based on the two most recent water level measurements.

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Chapter 4 Tables

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Table 4-1 Historical water-level measurements from the US Geological Survey (5 pages). TG Land Depth calc TG calc surface of Bottom Water Water Well elevation well well level Level log Measurement USGS Site Hydrologic Latitude Longitude (ft amsl) (ft elev (ft Date of (ft elev (ft found Agency number Site Name Unit NAD27 NAD27 NGVD29 bls) amsl) Measurement bls) amsl) Status ? Comments USGS 464133117142701 14N/44E-14P01 17060108 46°41'33" 117°14'27" 2550 600 1950 2/25/1959 236 2314 Y USGS states this is a GR well 2/27/1959 236 2314 3/26/1974 272.5 2277.5 6/3/1975 277 2273 R 3/9/1983 286 2264 2/22/1984 283 2267 2/21/1985 282 2268 9/9/1985 285 2265 USGS states this a Columbia River Basalt Group (122CBRV) local aquifer USGS 464444117142501 15N/44E-35E01 17060108 46°44'44" 117°14'25" 2420 300 2120 6/1/1954 89 2331 Y? well. 6/8/1954 88.87 2331.13 3/21/1973 123 2297 3/26/1974 125.3 2294.7 6/5/1975 126.9 2293.1 USGS 464710117150601 15N/44E-15G02 17060108 46°47'10" 117°15'06" 2390 290 2100 3/1/1969 146 2244 N 3/19/1969 146 2244 4/1/1974 160.2 2229.8 P 6/6/1975 158.1 2231.9 P USGS 464236117160001 14N/44E-09J02 17060108 46°42'36" 117°16'00" 2485 286 2199 1/17/1973 192.1 2292.9 N USGS states this is a W well 3/27/1973 192.2 2292.8 3/27/1974 193.2 2291.8 R 6/3/1975 194.1 2290.9 3/9/1983 193.4 2291.6 10/3/1983 197.13 2287.87 2/22/1984 206.1 2278.9 3/6/1985 205.33 2279.67 9/9/1985 206.7 2278.3

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Table 4-1 Historical water-level measurements from the US Geological Survey (5 pages). TG Land Depth calc TG calc surface of Bottom Water Water Well elevation well well level Level log Measurement USGS Site Hydrologic Latitude Longitude (ft amsl) (ft elev (ft Date of (ft elev (ft found Agency number Site Name Unit NAD27 NAD27 NGVD29 bls) amsl) Measurement bls) amsl) Status ? Comments USGS states this is a CRBG USGS 464643117180601 15N/44E-20D01 17060108 46°46'43" 117°18'06" 2342 280 2062 10/1/1974 130 2212 N well USGS states this is a CRBG USGS 464347117175101 14N/44E-05F01 17060108 46°43'47" 117°17'51" 2360 242 2118 8/1/1974 192 2168 N well USGS states this is a CRBG USGS 464654117172601 15N/44E-17R01 17060108 46°46'54" 117°17'26" 2340 180 2160 6/1/1975 127 2213 N well USGS states this is a CRBG USGS 464640117170701 15N/44E-21D01 17060108 46°46'40" 117°17'07" 2355 177 2178 7/1/1954 100 2255 N well 3/20/1973 131.97 2223.03 3/26/1974 132.9 2222.1 6/5/1975 132.03 2222.97 USGS states this is a CRBG USGS 464518117141601 15N/44E-26L01 17060108 46°45'18" 117°14'16" 2390 160 2230 7/1/1955 74 2316 N well 7/8/1955 73.55 2316.45 3/21/1973 102.8 2287.2 3/26/1974 105.4 2284.6 6/5/1975 106.4 2283.6

Reported water level, not Barker 1979 14N/44E-16P01 46°41'36" 117°16'29" 2318 140 2178 8/-/1974 2300 N measured by USGS personnel USGS 464031117162301 14N/44E-28A01 17060108 46°40'31" 117°16'23" 2385 111 2274 3/27/1974 42.6 2342.4 N 6/3/1975 43.8 2341.2 R Barker 1979 14N/44E-16Q01 46°41'31" 117°16'29" 2325 65 2260 N USGS states this is a CRBG USGS 464056117161301 14N/44E-21J01 17060108 46°40'56" 117°16'13" 2335 58 2277 8/1/1974 20 2315 N well

USGS states this is a CRBG USGS 464306117151501 14N/44E-10B02 17060108 46º43'06" 117º15'15" 2600 475 2125 8/1/1974 274 2326 Y well; owner provided well log

USGS 464304117151701 14N/44E-10B01 17060108 46º43'04" 117º15'17" 2605 330 2275 3/1/1973 277 2328 Y Owner provided well log 3/24/1973 276.73 2328.27 3/27/1974 285.5 2319.5 8/21/1974 279.1 2325.9 S USGS 464724117191202 15N/43E-13H02 17060108 46º47'24" 117º19'40" 2405 240 2165 3/9/1983 41.6 2363.4 Y 2/22/1984 41.5 2363.5

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Table 4-1 Historical water-level measurements from the US Geological Survey (5 pages). TG Land Depth calc TG calc surface of Bottom Water Water Well elevation well well level Level log Measurement USGS Site Hydrologic Latitude Longitude (ft amsl) (ft elev (ft Date of (ft elev (ft found Agency number Site Name Unit NAD27 NAD27 NGVD29 bls) amsl) Measurement bls) amsl) Status ? Comments 2/21/1985 43.72 2361.28 8/16/1985 N USGS 464522117162601 15N/44E-28K01 17060108 46º45'22" 117º16'26" 2398 222 2176 3/1/1973 66 2332 N

USGS 464330117140001 14N/44E-02K02 17060108 46º43'30" 117º14'00" 2480 203 2277 6/6/1975 20.3 2459.7 N USGS states this is a W well 3/1/1984 20.2 2459.8 3/6/1985 20.54 2459.46 8/16/1985 N USGS 464925117161301 15N/44E-04A01 17060108 46°49'25" 117°16'13" 2192 200 1992 8/1/1954 6 2186 N USGS states this is a CRBG USGS 463940117154101 14N/44E-34C01 17060108 46°39'40" 117°15'41" 2455 200 2255 1/1/1901 1 2454 N well 3/22/1973 0.86 2454.14 3/27/1974 F

USGS 464313117151901 14N/44E-03P01 17060108 46º43'13" 117º15'19" 2650 176 2474 8/1/1954 110 2540 Y Owner provided well log 3/22/1973 102.35 2547.65 USGS states this is a CRBG well. The well log pdf associated with this address is USGS 464457117162101 15N/44E-33B01 17060108 46º44'57" 117º16'21" 2430 175 2255 1/1/1944 60 2370 N incorrect. 6/1/1944 60 2370 3/20/1973 97.75 2332.25 USGS states this is a CRBG USGS 464848117180301 15N/44E-05L01 17060108 46°48'48" 117°18'03" 2418 170 2248 1/1/1931 28 2390 N well 10/1/1931 28 2390 3/20/1973 60.57 2357.43 3/26/1974 60.38 2357.62 USGS states this is a CRBG USGS 464053117121801 14N/44E-24J01 17060108 46°40'53" 117°12'18" 2620 162 2458 1/1/1951 60 2560 N well 9/1/1951 60 2560 4/1/1972 40 2580 3/22/1973 45.59 2574.41 3/27/1974 42.8 2577.2

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Table 4-1 Historical water-level measurements from the US Geological Survey (5 pages). TG Land Depth calc TG calc surface of Bottom Water Water Well elevation well well level Level log Measurement USGS Site Hydrologic Latitude Longitude (ft amsl) (ft elev (ft Date of (ft elev (ft found Agency number Site Name Unit NAD27 NAD27 NGVD29 bls) amsl) Measurement bls) amsl) Status ? Comments USGS 464742117234001 15N/43E-16A01 17060108 46°47'42" 117°23'40" 2200 138 2062 6/13/1974 81 2119 Y USGS 464621117115101 15N/45E-19E01 17060108 46º46'21" 117º11'51" 2430 134 2296 5/1/1954 56 2374 N 5/27/1954 57.04 2372.96 3/21/1973 45.53 2384.47 USGS states this is a CRBG USGS 464630117163201 15N/44E-21C01 17060108 46º46'30" 117º16'32" 2365 130 2235 1/1/1948 30 2335 N well 3/1/1948 30 2335 3/20/1973 34.44 2330.56 3/26/1974 23.6 2341.4 USGS 464930117171501 15N/44E-05A01 17060108 46°49'30" 117°17'15" 2358 120 2238 1/1/1915 60 2298 N 3/20/1973 23.58 2334.42 3/26/1974 23.1 2334.9 USGS 464940117234001 16N/43E-33R01 17060108 46°49'40" 117°23'40" 2220 116 2104 8/7/1975 6 2214 USGS states this is a Saddle Mountain Basalt Formation well.The well log pdf associated with this address is USGS 464724117191201 15N/43E-13H01 17060108 46º47'24" 117º19'40" 2405 112 2293 8/18/1954 15 2390 N incorrect. USGS 464445117140601 15N/44E-35F01 17060108 46º44'45" 117º14'06" 2435 96 2339 3/1/1973 16 2419 N 3/21/1973 15.89 2419.11 3/26/1974 13.7 2421.3 USGS 464332117142201 14N/44E-02M01 17060108 46º43'32" 117º14'22" 2502 93 2409 1/1/1950 48 2454 N 3/1/1950 48 2454 3/27/1974 32.6 2469.4 USGS states this is a Saddle Mountain Basalt Formation USGS 464643117184701 15N/44E-19B01 17060108 46º46'43" 117º18'47" 2380 91 2289 8/19/1954 18 2362 N well 3/9/1983 25.7 2354.3 10/3/1983 27.08 2352.92 3/1/1984 21.1 2358.9 3/6/1985 21.42 2358.58

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Table 4-1 Historical water-level measurements from the US Geological Survey (5 pages). TG Land Depth calc TG calc surface of Bottom Water Water Well elevation well well level Level log Measurement USGS Site Hydrologic Latitude Longitude (ft amsl) (ft elev (ft Date of (ft elev (ft found Agency number Site Name Unit NAD27 NAD27 NGVD29 bls) amsl) Measurement bls) amsl) Status ? Comments 8/16/1985 N USGS states this is a CRBG USGS 464328117135101 14N/44E-02K01 17060108 46º43'28" 117º13'51" 2510 79 2431 8/1/1954 15 2495 N well 3/24/1973 26.92 2483.08 3/27/1974 26.5 2483.5 R 6/6/1975 20.3 2489.7 USGS 464541117162401 15N/44E-28B02 17060108 46º45'41" 117º16'24" 2380 70 2310 3/1/1973 36 2344 N 3/22/1973 35.53 2344.47 3/26/1974 23.4 2356.6 USGS states this is a CRBG USGS 464140117134401 14N/44E-14J01 17060108 46°41'40" 117°13'44" 2545 62 2483 3/26/1974 8.25 2536.75 N well This well is completed in the Columbia Plateau basaltic- rock aquifers 14N/44E-16P01 (N600CMBPLV) national USGS 464134117165601 LE12 17060108 46°41'32.95" 117°16'59.82" 2325 60 2265 5/29/1990 32 2293 N aquifer.

This well is completed in the Saddle Mountains Basalt Formation (122SDLM) local aquifer. The well log pdf associated with this address is 6/28/1993 31.8 2293.2 incorrect.

F = The site was flowing. Water level or head could not be measured without additional equipment. N = The measurement was discontinued. P = The site was being pumped. R = The site had been pumped recently. S = A nearby site that taps the same aquifer was being pumped. amsl = above mean sea level bls = below land surface

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Table 4-2 Wells in the program that were not able to be measured in 2010.

Site Name Comments Permission declined or no contact info 15N/44E-15G02 US Bank listed as contact - no idea about well. Owner says that well is shallow and does not go into the aquifer 14N/44E-09J02 - well drilled to 66 feet, pump set at 62 feet (no) 15N/44E-17R01 No, too busy 15N/44E-21D01 No 14N/44E-28A01 Too busy 16N/43E-33R01 No contact information found. Assessor’s office ownership incorrect; not able to reach 15N/45E-19E01 potential owner. 14N/44E-16Q01 Not known who owns well property 14N/44E-34C01 15N/44E-05L01

Could not reach 14N/44E-14P01 15N/44E-20D01 15N/44E-04A01 14N/44E-02K01 15N/44E-28B02

Well abandoned or not found 15N/43E-13H01 Well no longer known by owner.

14N/44E-16P01 Next to 16P01 LE12 - thought same well. 14N/44E-14J01 Well is sealed; no longer in use.

14N/44E-02K02 Well is dry and abandoned. Property on spring water. 14N/44E-21J01 Well went dry in 1970s; owner dug out well. Owner says well was drilled down to 180 feet. Though owner willing participant, could not meet field technician in the field; 15N/43E-16A01 could not find well. Other 15N/43E-13H02 Incorrect setting used on sonic device. Access was a 2 inch pipe protruding from the top of the well cap with a metal cap on the top. Pipe cap was rusted on. 15N/44E-28K01 Attempts to remove failed. Did not measure because in underground bunker - enclosed 15N/44E-35F01 space. Measured a well near this location but does not match up with 14N/44E-16P01 LE12 bottom hole elevation for 16P01 or 16P01 LE12.

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Table 4-3 Well and water-level measurement data for wells measured in 2010 (2 pages). Water- Water-level level depth Water-level Sonic Sonic Sonic Measurement depth from E-tape E-tape from depth from Date Device Device Device Other point - ground ground Well location ID Type of well DTW (ft) DTW (ft) ground ground Comments measured DTW (ft) DTW (ft) DTW (ft) DTW (ft) surface (neg if surface (TOC) 1st (TOC) 2nd surface surface using (TOC) 1st (TOC) 2nd (TOC) 3rd (TOC) bgs) using sonic attempt attempt using e- Other (ft) attempt attempt attempt device (ft) tape (ft)

Owner thinks well collapsed - one day no water. Could explain why different readings between sonic device and e-tape. Well in 2 inches above pump house; concrete floor few inches below 14N/44E-10B01 Domestic 6/29/2010 193.60 193.59 201.0 201.1 201.1 concrete floor 193.43 200.9 ground surface Tested sonic device reading by conducting drawdown test. Confident device is reading 14N/44E-10B02 Domestic 6/29/2010 294.7 294.7 1 ft 293.7 water level.

14N/44E-02M01 Domestic 6/29/2010 36.02 36.4 36.4 36.4 1 ft 35 35 Could not use e-tape due to small access hole in well cap. Well near house owned/rented by someone else. Did not conduct drawdown 14N/44E-03P01 ? 6/29/2010 103.5 103.5 103.5 -3.6 ft 107.1 test.

Used a garden hose to measure because pipe at 15N/44E-35E01 Irrigation 6/30/2010 42 3 inches 41.8 surface is at an angle.

Well no longer used because high nitrates. Solid e-tape reading. Unsure why sonic device 15N/44E-26L01 Domestic 6/29/2010 140.87 58.2 58.2 58.2 -4.09 ft 144.96 62.3 and e-tape reading are so different. Did not use e-tape; sonic device: 261.8 ft (deep setting), 12.6 ft (normal setting). Well about 3 feet only 180 feet deep so did not use deep setting Harlow Domestic 6/29/2010 12.6 high. 9.6 sonic reading.

Henson Domestic 6/29/2010 78.20 78.6 78.6 78.6 1 ft 77 78 New well drilled in 1982 Great difficulty accessing well because concrete plug over top that needed to be removed by a tractor and another machine to remove the collar over the well. Owner had pump replaced by TPM Systems in Lewiston, ID. They provided the depth to water taken by at ground observing the water mark on the pipe when 14N/44E-05F01 ? 8/5/2009 199 surface 199 pulling the pump.

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Table 4-3 Well and water-level measurement data for wells measured in 2010 (2 pages). Water- Water-level level depth Water-level Sonic Sonic Sonic Measurement depth from E-tape E-tape from depth from Date Device Device Device Other point - ground ground Well location ID Type of well DTW (ft) DTW (ft) ground ground Comments measured DTW (ft) DTW (ft) DTW (ft) DTW (ft) surface (neg if surface (TOC) 1st (TOC) 2nd surface surface using (TOC) 1st (TOC) 2nd (TOC) 3rd (TOC) bgs) using sonic attempt attempt using e- Other (ft) attempt attempt attempt device (ft) tape (ft)

232.6 232.6 d/16.8 232.6 Owner says well originally dug in 1877. Well 15N/44E-33B01 ? 7/17/2010 131.3 131.3 d/16.8 n n d/16.8 n 10 inches 130.4 Not using is not in use and no pump.

A newer well was dug on the property in 1979. Cap was bolted on. Cascading water could be heard. A pump was installed at this well. No Small Domestic 7/17/2010 121.65 3.75 feet 117.90 sonic measurement because of wiring.

255.6 255.6 d/43.6 255.6 Shallow measurement corresponds to previous 14N/44E-24J01 Domestic 7/23/2010 d/43.6 n n d/43.6 n -5 feet 48.6 measurements.

Opening too narrow for e-tape. Based on 231.6 231.6 d/34.2 231.6 previous measurements by owner and USGS, 15N/44E-21C01 Domestic 7/16/2010 d/34.2 n n d/34.2 n 4 inches 33.9 34.2 feet should be the correct depth.

Well cap had an access port at 1 inch in diameter. Pipe blocking the port required the use of the sonic device placed at an angle. Measurements may be questionable because of configuration. Deep setting on sonic device 15N/44E-05A01 Domestic 7/26/2010 26.3 n 26.3 n 26.3 n -4.15 feet 30.5 did not produce any measurement.

Top of well was visible, no cap present. Water surface was visible at the top of the well; no measurement taken. Home is surrounded by large gardens. Owner says that sprinklers are run at night. USGS states may be Saddle water is at Mountains well which would explain the 15N/44E-19B01 Domestic 7/16/2010 top of well -4.7 feet 4.7 shallow water level.

233.6 233.8 d/31.2 233.8 McKeirnan ? 7/23/2010 30.56 30.56 d/31.2 n n d/31.2 n 2.5 feet 28.1 28.7 E-tape probe came up very muddy. n = near surface setting DTW = depth to water bgs = below ground surface d = deep setting TOC = top of casing ft = feet

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Table 4-4 Rates of water-level decline (2 pages).

Water level Drawdown rate Drawdown elevation (feet/year) from since first Time from first Date of (feet amsl) previous. measurement measurement to Well Location ID Measurement TG calc. measurement (feet) recent (years) 15N/44E-35E01 6/1/1954 2331 6/8/1954 2331.13 3/21/1973 2297 1.82 3/26/1974 2294.7 2.27 6/5/1975 2293.1 1.34 6/30/2010 2378.2 -2.42 -47.20 56.12 14N/44E-05F01 8/1/1974 2168 8/5/2009 2161 0.20 7.00 35.04 15N/44E-26L01 7/1/1955 2316 7/8/1955 2316.45 3/21/1973 2287.2 1.65 3/26/1974 2284.6 2.56 6/5/1975 2283.6 0.84 6/29/2010 2245.04 1.10 70.96 55.03 14N/44E-10B02 8/1/1974 2326 6/29/2010 2307 0.53 19.00 35.93 14N/44E-10B01 3/1/1973 2328 3/24/1973 2328.27 3/27/1974 2319.5 8.70 8/21/1974 2325.9 -15.89 6/29/2010 2411.6 -2.39 -83.60 37.35 14N/44E-03P01 8/1/1954 2540 3/22/1973 2547.65 -0.41 6/29/2010 2542.9 0.13 -2.90 55.95 15N/44E-33B01 1/1/1944 2370 6/1/1944 2370 3/20/1973 2332.25 1.31 7/17/2010 2299.6 1.01 70.40 66.59 14N/44E-24J01 1/1/1951 2560 9/1/1951 2560 4/1/1972 2580 -0.97 3/22/1973 2574.41 5.75 3/27/1974 2577.2 -2.75 7/23/2010 2571.4 0.16 -11.40 59.60 15N/44E-21C01 1/1/1948 2335 3/1/1948 2335 3/20/1973 2330.56 0.18 3/26/1974 2341.4 -10.66 7/16/2010 2331.1 0.28 3.90 62.58 15N/44E-05A01 1/1/1915 2298 3/20/1973 2334.42 -0.63

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Table 4-4 Rates of water-level decline (2 pages).

Water level Drawdown rate Drawdown elevation (feet/year) from since first Time from first Date of (feet amsl) previous. measurement measurement to Well Location ID Measurement TG calc. measurement (feet) recent (years) 3/26/1974 2334.9 -0.47 7/26/2010 2327.5 0.20 -29.50 95.63 14N/44E-02M01 1/1/1950 2454 3/1/1950 2454 3/27/1974 2469.4 -0.64 6/29/2010 2467 0.07 -13.00 60.53 15N/44E-19B01 8/19/1954 2362 3/9/1983 2354.3 0.27 10/3/1983 2352.92 2.42 3/1/1984 2358.9 -14.55 3/6/1985 2358.58 0.32 8/16/1985 7/16/2010 2375.3 -0.66 -13.30 55.95 TG = TerraGraphics amsl = above mean sea level Negative drawdown rate indicates water-level rise Significant digits for drawdown rate should coincide with water level elevation - kept to hundredths to show small changes

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Section 5.0 Task 4.5 – Preliminary Data-Gap Investigation: Surface- Water / Ground-Water Interaction

5.1 Introduction

The hydraulic connection of surface water and ground water was also identified as a data gap early in the Framework Project. Changing project scope allowed inclusion of an analysis of ground-water levels in response to changes in stream flow in the Framework Project. In this case, the analysis was based on existing data; no new data were collected. The purpose of the surface-water/ground-water interaction project is to compare stream-flow records to hydrographs from selected wells to ascertain the degree of hydraulic connection of surface water and ground water at selected sites within the Palouse Basin. The analysis includes consideration of four stream segments. The stream segments within the Pullman-Moscow subarea are the South Fork of the Palouse River in Pullman in connection to the lower aquifer and Paradise Creek in Moscow in connection with the upper aquifer (Figure 5-1). Within the northern subarea, analysis includes the Palouse River in Palouse in connection to the lower aquifer. The fourth study area, within the western subarea, is an analysis of Union Flat Creek at Klemgard Park in connection to a well completed in Grande Ronde Formation basalt. This formation hosts the lower aquifer in the other subareas. However, it is unknown whether the conceptual model of an upper aquifer and a lower aquifer is applicable to this portion of the western subarea. These stream segments were selected for analysis because of the availability of water-level data from wells located near the streams and the availability of stream discharge records (except in the case of Union Flat Creek). Table 5-1 lists the information available on the wells discussed in the study. Ground-water levels are below stream elevation at the study locations in Pullman, Palouse, and Moscow. Thus, the objective of the investigation in these areas is to identify the degree to which the aquifer receives recharge from the surface-water system. The focus of this study is on periods of high flow within each of the target streams. Recharge from a surface stream to a hydraulically interconnected ground-water system is greatest during high-flow events because of three factors: 1) the higher stream stage increases the downward hydraulic gradient if there is saturated hydraulic connection to the aquifer; 2) there is greater wetted perimeter for the stream during high flow and thus greater cross-sectional area for leakage; and 3) greater water velocity in the stream during high flow events tends to scour bed sediment and has the potential to increase vertical hydraulic conductivity between the stream and the aquifer. It is unlikely that stream discharge changes during low-flow periods will cause changes in ground-water levels if ground-water responses are not detectable during high-flow events.

5.2 Hydrogeologic Conceptual Model of a Losing Stream

The hydraulic interaction of surface water and ground water at a specific location depends on both hydrogeologic and hydraulic characteristics. The hydrogeologic characteristics are primarily the vertical and horizontal hydraulic conductivity of the layers of geologic material underlying the stream. The hydraulic characteristics include the vertical and horizontal hydraulic

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Palouse Ground Water Basin Framework Project FINAL report gradient and the degree to which the vertical flow is saturated, intermittently saturated, or unsaturated. A study of surface-water/ground-water interaction of the Spokane River and the Spokane Valley/Rathdrum Prairie aquifer in northern Idaho and eastern Washington provides insight relative to the pattern of water-level response that might be expected in aquifers within the Palouse Basin from changes in stream flow. Caldwell and Bowers (2003, pages 14-15) provide the following description of the losing reach of the Spokane River that was the focus of their study effort. “The conceptual model for the losing section of the Spokane River between Post Falls and Spokane is either that the river is separated from the ground-water system by an unsaturated zone or that the zone beneath the river is saturated and the hydraulic gradient from the river to the aquifer is steep. The streambed of the Spokane River along this reach is composed primarily of cobbles and boulders … Below the surface of the streambed, the coarse material contains interstitial fine silt and clay… The fine-grained material, some of which may have been transported with the leaking water from the river, likely reduces the permeability of the streambed and underlying substrate. This zone of reduced permeability acts as a leaky layer between the river and the underlying aquifer…. “The rate at which water flows between the river and the aquifer is dependent upon several factors including the hydraulic properties of the streambed and the adjoining aquifer, and the hydraulic gradient between the river and aquifer… “When the water table is below the streambed, unsaturated conditions exist below the river, and leakage from the river is unaffected by the hydraulic head in the aquifer. In other words, the amount of leakage from the river remains the same regardless of how far the water table is below the river bottom…. “The occurrence and magnitude of fluctuations in ground-water levels in response to changes in river state are indicators of the relation between the ground water and the river…. A ground-water level rise in response to an increase in river stage is consistent with increased recharge to the aquifer from river leakage. Therefore, water-level fluctuations in the near-river aquifer in response to changes of river stage are expected if the river is a local source of recharge to the aquifer.” The water-level responses in wells completed in the Spokane Valley/Rathdrum Prairie aquifer to a flood event in the Spokane River serve as an example of how hydrographs can be interpreted in the Palouse Basin. Figure 5-2 shows a plot of river stage during the 2001 water year along with the hydrographs for wells located 100 feet and 475 feet from the Spokane River. Also shown on the graph is the daily mean stream-flow loss in the river calculated between the Post Falls, Idaho and Spokane, Washington USGS flow-measurement stations. The following observations may be drawn from Figure 5-2.  The water-level elevations in the wells 100 feet and 475 feet from the river are about 25 feet and 45 feet lower than the river, respectively. This indicates this is a losing reach of the river and that the hydraulic gradient in the aquifer is away from the river.  Short-term variations in river stage, such as during April and May 2001, are reflected in the shallow well located 100 feet from the river but are minor to non-detectable in the well located 475 feet from the river.

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 The longer-term stage patterns in the river, such as the high-flow event in April-May 2001, are reflected in both wells. The example from the Spokane Valley/Rathdrum Prairie aquifer is different from the selected sites within the Palouse Basin in the following ways.  Both the upper and lower aquifers in the Palouse Basin act as confined during short-term aquifer tests because of the presence of overlying aquitards (dense basalt and fine-grained sediment). The Spokane Valley/Rathdrum Prairie aquifer acts as unconfined under both short- and long-term conditions.  The Spokane River is a much larger recharge source than any of the streams selected for analysis within the Palouse Basin. Stream flow rather than stream stage data are used for the analysis of hydraulic connection of surface water and ground water in the Palouse Basin because that is the form of data available. The variations in flow typically are much greater than the variations in stream stage. However, the timing of peaks in stream stage and stream flow is the same.

5.3 South Fork of the Palouse River in Pullman Relative to the Lower Aquifer

5.3.1 Hydrogeologic Setting The focus of this analysis is on the hydraulic connection of the lower aquifer to the reach of the South Fork of the Palouse River near the WSU campus. A data gap identified during the synthesis task and discussed in the Data Gap section of this report (Section 6.0) addresses the potential for stream loss to the upper and/or lower aquifer along a reach of the South Fork northwest of the center of Pullman. The lower aquifer is the water supply source for Pullman and WSU. The overlying upper aquifer is utilized only by domestic and other small-yield wells in the Pullman area. Figure 5-3 shows the location of wells completed in the lower aquifer in the immediate Pullman area and the location of the USGS gaging station on the South Fork of the Palouse River (South Fork), USGS ID 13348000. Figure 5-4 shows two geologic cross sections within the city of Pullman. The contact between the Wanapum Formation and the Grande Ronde Formation (approximately the division between the upper and lower aquifers) is close to land surface along the South Fork in Pullman, particularly near the location of the WSU test well. The elevation of the USGS stream station on the South Fork is 2,326 feet. The water-level elevation in the lower aquifer in the Pullman area in late 2009 was about 2,244 feet. Thus, the South Fork is a losing stream relative to the lower aquifer in this reach. The amount of stream loss depends mostly on the vertical hydraulic conductivity of geologic material between the stream and the aquifer. This analysis of surface-water/ground-water connection in the vicinity of WSU in downtown Pullman is focused on the lower aquifer.

5.3.2 Hydrograph Analysis Hydrographs for two wells within Pullman (WSU test well and Pullman well #8) and one well near the river about 3 miles southeast of Pullman (Cornelius well) are compared to the flow record for the South Fork. Figure 5-5 includes the hydrographs for the WSU test well and Pullman well #8 along with the discharge record of the South Fork for the period of 2006 through 2009 (USGS, 2010). The WSU test well is 144 feet deep, open at the bottom of the

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Palouse Ground Water Basin Framework Project FINAL report borehole (although there is evidence of cascading water down the well), and is located about 500 feet east of the South Fork at an approximate elevation of 2,364 feet. This gives a bottom-hole elevation of about 2,220 feet. Pullman well #8 is 793 feet deep, has screen sections between the depths of 296 feet and 793 feet and is located about 1,800 feet west-southwest of the South Fork at an approximate elevation of 2,513 feet. This gives a bottom-hole elevation of about 1,720 feet. The Cornelius well is 245 feet deep and is located near the South Fork at a site about 6 miles southeast of Pullman. It has a top of casing elevation of 2,455 feet and a bottom-hole elevation of approximately 2,207 feet (assuming the casing is 3 feet above ground surface). The South Fork has a spring high flow period when discharges exceed 100 cubic feet per second for a month or more followed by a decrease to the summer base flow period when discharge typically is less than 5 cubic feet per second (Figure 5-5). The annual peak discharge in the South Fork was 452 cubic feet per second on January 18, 2006, 516 cubic feet per second on January 3, 2007, 480 cubic feet per second on March 1, 2008, and 1,180 cubic feet per second on January 8, 2009. Logically, the greatest recharge from the South Fork should occur in the spring when the ground is thawed, there is an extended period of high flow, and the peak flow events occur. The increased recharge occurs because of greater wetted perimeter of the stream as well as a higher river stage and thus a higher vertical gradient. The hydrograph for the WSU test well shows the following annual water-level pattern (Figure 5- 5). The water levels start dropping in May-June and reach an annual low in September-October. This is likely related to greater pumping from the lower aquifer by both Pullman and WSU wells during the summer months. The water levels rise starting in September-October and peak in December-January. This is followed by a small downward trend in water levels that occurs from December-January until May-June. This downward trend is similar to the long-term rate of water-level decline in the aquifer of slightly less than 1.0 feet per year. There is no discernible impact of high flow in the South Fork on the water-level in the WSU test well during the period of record shown in Figure 5-5. The high flow period in 2008 occurred during the recession period of December-January to May-June. If recharge does occur to the lower aquifer from spring high flow events, it is small enough to be indiscernible in the water-level record of the WSU test well. The hydrograph for Pullman well #8 also does not show an impact from recharge associated with the 2009 high flow event in the South Fork (Figure 5-5). The water levels in the well continued to recover during the entire high flow event. The lack of response in the lower aquifer to flow events in the South Fork is consistent with Russell’s (1897) observation that shallow wells, similar to the WSU test well, flowed at land surface in the 1890s. The confining layer, necessary for the existence of flowing wells, would isolate surface streams from the lower aquifer in the immediate Pullman area. The Cornelius well is about 245 feet deep. A comparison of the hydrograph for the Cornelius well to stream flow information for the gaging station located in Pullman is assumed to be valid because of the relatively short travel time in the river between the Cornelius well site and the gage site. The hydrograph for the Cornelius well (Figure 5-6) is very similar to the WSU test well. An impact on the lower aquifer associated with recharge from the South Fork in the vicinity of the Cornelius well is not discernible in the hydrograph.

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5.4 Palouse River in the City of Palouse Relative to the Lower Aquifer

5.4.1 Hydrogeologic Setting The lower aquifer is the water-supply source for two City of Palouse wells. The overlying upper aquifer is utilized by domestic wells in the general area. Figure 5-7 shows the location of two City of Palouse wells relative to the Palouse River. The USGS gaging station on the Palouse River is located about 6 miles east, USGS ID 13345000. Comparison of the hydrograph for the City of Palouse wells to stream flow information for the gaging station located near Potlatch is assumed to be valid because of the relatively short travel time in the river between the two sites. Two geologic cross sections provide information of the subsurface geology in the vicinity of the city of Palouse (Figures 5-7 and 5-8). The top of the Grande Ronde Formation, which in this area likely is the top of the lower aquifer, is hundreds of feet below the Palouse River in the area of the city wells. This makes it extremely unlikely that changes in stage in the river would result in water-level changes in wells completed in the lower aquifer. It is more likely that a hydraulic connection exists between the river and the upper aquifer. However, the temporal water-level data are not available for upper aquifer tests to allow an analysis of this potential hydraulic connection.

5.4.2 Hydrograph Analysis The Palouse River at Potlatch has a spring high flow period when discharges exceed 500 cubic feet per second for several months, followed by a decrease to the summer base-flow period when discharge typically is less than 5 cubic feet per second. The river discharge for water years 2007-2008 and 2008-2009 (USGS, 2010) along with water-level data for the two City of Palouse wells are given on Figures 5-9 and 5-10. The annual peak discharge in the Palouse River was 1,920 cubic feet per second on April 4, 2008 and 4,070 cubic feet per second on January 8, 2009. If there is a hydraulic connection of the lower aquifer with the Palouse River, the aquifer water- level response should occur in the spring when there is an extended period of high flow and when the peak flow events occur. The hydrographs for the two City of Palouse wells track very similarly. The short-term fluctuations shown are associated with operation of the wells. The lowest water levels in the annual cycle occur in August-September at the end of the period of greatest withdrawal. The non-pumping water levels remain nearly constant during the winter months. Note that the winter water levels in 2009 are about 0.5 feet lower than the winter levels of 2008. This probably represents the long-term rate of water-level decline. There is no discernible impact of high flow in the Palouse River on the water level in either of the City of Palouse wells during the period of record shown in Figures 5-9 and 5-10. If recharge does occur to the lower aquifer from spring high flow events, it is small enough to be indiscernible in the water-level record.

5.4.3 Aquifer Water-Temperature Analysis Gregory (personal communication, 2010) identified an unusual pattern of ground-water temperature while evaluating the data logger record from the City of Palouse well #3. The data logger records at this well show a change in water temperature when the well is being pumped versus when it is not being pumped. The temperature data also show a change from winter to

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Palouse Ground Water Basin Framework Project FINAL report summer. Figure 5-11 is a plot of depth to water and water temperature during the winter of 2008; Figure 5-12 is a similar plot for the summer of 2008. Gregory theorized that the temperature changes in the well may reflect a hydraulic connection with the Palouse River. The following is an analysis of the water-level and temperature data from City of Palouse well #3.  The water well report for Palouse well #3 shows the following information: 1) the well was drilled to a depth of 460 feet and penetrated basalt from 3 to 188 feet, mostly sand and clay from 188 to 395 feet and basalt from 396 to 460 feet; 2) water-producing zones were noted in fine sand in the depth range of 188 to 218 feet and in basalt in the depth range of 402 to 435 feet; 3) the well was completed with solid casing to 400 feet and a screen in the depth interval of 397 to 432 feet; 4) the well seal was placed to a depth of 400 feet; and 5) the reported static depth to water when drilled was 250 feet. The hydrographs show that the static and pumping depth to water values are about 260 and 265 feet respectively.  The water-level data on Figure 5-11 show that the Palouse well #3 is typically pumped only two times a week during the winter. The small fluctuations between the on-cycles probably represent operation of City of Palouse well #1. The water temperature as recorded by the data logger increases from 8 or 9 degrees C when the well is off to more than 13 degrees C when the well is being pumped.  Well #3 for the City of Palouse is pumped more often during the summer, as the water- level data on Figure 5-12 show. In this case, the water temperature ranges from 15 or 16 degrees C when the well is not being pumped and decreases to slightly more than 14 degrees during well operation.  For comparison, data-logger records for IDWR-4 (an observation well located northwest of Moscow and completed in the lower aquifer) show a total change of less than 0.5 degrees C over a period of record from April through November 2008. Well INEL-D, located at the UI Groundwater Field Laboratory and completed in the lower portion of the upper aquifer, also had a temperature variation of less than 0.5 degrees C. Data from both of these wells fit the temperature pattern that would be expected for ground water from a deep aquifer system.  The data-logger temperature measurement represents water between the pump column and the well casing at a depth of about 300 feet (which is about 100 feet above the top of the aquifer). The temperature recorded by the data logger likely represents the water and rock temperature outside the well casing at the depth of the data logger when the well is not being pumped. The water temperature in the space between the pump column and the well casing appears to adjust to near the temperature of the water within the pump column when the well is being pumped. The hydrographs for January-February and August-September indicate that the water temperature measured by the data logger had not yet equilibrated to the pumped water temperature by the end of each pumping cycle. Likely, the temperature of the water in the aquifer in the depth range of 400 to 432 feet is near 14 degrees C and probably does not change significantly throughout the year. The ground-water temperature in well IDWR-4 was between 13 and 14 degrees C for the 2008 period of record.

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 In summary, the water temperature in the aquifer penetrated by Palouse well #3 probably is relatively constant throughout the year at about 14 degrees C. The data logger readings likely reflect water temperature influences from the rock and water outside of the casing when the well is not pumping and the temperature of water within the pump column when the well is being pumped. Thus, the temperature data from Palouse well #3 do not provide evidence for a hydraulic connection between the Palouse River and the lower aquifer at the city of Palouse.

5.5 Paradise Creek in Moscow Relative to the Upper Aquifer

5.5.1 Hydrogeologic Setting The geologic section under the western side of Moscow consists of basalt flows layered with sedimentary units. Figure 5-13 shows the locations of two geologic cross sections, several wells, and the USGS gaging station on Paradise Creek, USGS ID 13346800. Figure 5-14 is a cross section oriented approximately south-southwest to north-northeast through the IDWR well #4, which is located about 1 mile north of Paradise Creek just east of the state line. Paradise Creek is located near the south (left) end of the section (near the notation of Moscow well #9). The cross-section shows that the uppermost basalt flow (Wanapum Formation) is overlain by thin cover of sediment and underlain by a sequence of sediment and basalt (Grande Ronde Formation). At this site, the upper aquifer starts at the top of the Wanapum Formation basalt flow and extends down to the top of the uppermost Grande Ronde Formation basalt flow. The lower aquifer underlies the upper aquifer. Figure 5-15 is a more detailed cross section of the south (left) portion of the cross section shown in Figure 5-13 and is based on local wells not shown on Figure 5-13. As is shown on Figure 5-15, the INEL-D well located at the UI Groundwater Field Laboratory is completed near the bottom of the Wanapum Formation basalt layer and penetrates the lower portion of the upper aquifer. Shallower wells are completed within the upper portion of the upper aquifer, in the E and W fracture zones in the Wanapum Formation basalt. Given the hydrogeologic setting of the Moscow area, it is logical to evaluate the potential hydraulic connection of Paradise Creek with the upper aquifer. There is no opportunity for a direct hydraulic connection between Paradise Creek and the lower aquifer. The current water- level elevation in wells completed in the upper and lower portions of the upper aquifer are lower than the elevation of Paradise Creek near the Idaho/Washington state line. Thus, there is a downward hydraulic gradient between the stream and the upper aquifer. The focus of this analysis is on wells completed in the lower portion of the upper aquifer. Previous investigators have shown that wells completed in the upper portion of the upper aquifer (E and W fractures zones at the UI Groundwater Field Laboratory) show water-level responses to flow changes in Paradise Creek (Li, 1991; Hernandez, 2007). Analysis locations were selected because of the proximity of wells with data-logger records and the availability of stream flow information from the USGS gaging site.

5.5.2 Hydrograph Analysis for High Flow Events in Paradise Creek The focus of this portion of the analysis is on ground-water level responses in the lower portion of the upper aquifer to major flow events within Paradise Creek. A later subsection of this section of the report addresses apparent responses identified by Robischon (personal

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Palouse Ground Water Basin Framework Project FINAL report communication, 2010) of the upper aquifer to low-flow events in the absence of responses to high-flow events. Paradise Creek at Moscow has a spring high-flow period when discharges exceed about 20 cubic feet per second for a month or more, followed by a decrease to the summer base-flow period when discharge typically is less than 1 cubic feet per second. Typically, there are two or more short-term, high-flow events each year. The creek discharge for the 2006 to 2010 period (USGS, 2010) is presented in Figure 5-16 along with water-level data for the two wells (INEL-D and IDWR-3). Well INEL-D is completed opposite the lower portion of the upper aquifer and is located within about 50 feet of the creek near the gaging station. Well IDWR-3 is also completed opposite the lower portion of the upper aquifer and is located about 1 mile north of the creek and gaging station. The greatest recharge from Paradise Creek should occur in the spring when there is an extended period of high flow and when the peak flow events occur. The hydrographs for the two wells completed in the lower portion of the upper aquifer track very similarly and show impacts from operation of production wells, likely Moscow wells #2 and #3 (Figure 5-16), although short-term aquifer tests between the Moscow wells #2 and #3 and the IDWR wells do not show evidence of connection (Robischon, personal communication, 2010). Peak ground-water levels occur in May of most years, with lowest water levels in late August or early September. The peak flow in Paradise Creek occurs in the period of late January to early March. A more detailed comparison of the well hydrographs to the discharge plot is shown in Figure 5-17 for the 2007-2008 water year. There is no discernable change in the rising slope of the ground-water levels in response to the high flow event in Paradise Creek that started in February 2008 and extended into April 2008. If recharge does occur to the upper aquifer from spring high flow events in Paradise Creek, it is small enough to be indiscernible in the water- level record.

5.5.3 Hydrograph Analysis for Low Flow Events in Paradise Creek Robischon (2010b) identified an August 2008 water-level pattern in wells completed in the lower portion of the upper aquifer that he postulated could be a response to a summer precipitation and associated runoff event in Paradise Creek. Figure 5-17 shows a comparison of the hydrograph for well INEL-D at the UI Groundwater Field Laboratory and discharge in Paradise Creek. A ground-water peak appears to lag the precipitation/stream-flow event by about three weeks. Robischon showed a similar response pattern in other wells completed in the lower portion of the upper aquifer in the western part of Moscow. He observed that wells completed in the lower portion of the upper aquifer in the central and eastern portions did not show an apparent response to the precipitation/stream-flow event. No explanation has been forwarded why wells such as INEL-D would respond to a small precipitation/runoff event during the summer and not respond to major spring runoff events.

5.6 Union Flat Creek at Klemgard Park Relative to a Well Completed in Basalt of the Grande Ronde Formation

5.6.1 Hydrogeologic Setting The Klemgard Park site on Union Flat Creek was added to the analysis of the hydraulic connection of surface water and ground water within the Palouse Basin based on information

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Palouse Ground Water Basin Framework Project FINAL report supplied by the Washington Department of Ecology (Gregory, personal communication, 2010). The park is located about 8 miles west-southwest of Albion (Figure 5-18). The Klemgard Park well, located near Union Flat Creek, was drilled to a depth of 150 feet and penetrated basalt below a depth of about 9 feet. The surface seal in the well extends to a depth 60 feet bgs. The casing is perforated in the depth range of 130 to 150 feet. According to Heinemann (1994), the lower portion of the basalt penetrated by the park well is part of the Grande Ronde Formation. Cross section C-D prepared by Heinemann (1994; his Figure 8) shows that the dip of the top of the Grande Ronde Formation is approximately the same as the gradient of Union Flat Creek. The Grande Ronde Formation hosts the lower aquifer in the Pullman-Moscow and northern subareas of the Basin. The application of the two-aquifer conceptual model to the western subarea is limited because of the lack of hydrogeologic information. Heinemann’s (1994) cross section shows an estimated “Grande Ronde potentiometric surface” or water level that when extrapolated to the southeast is below the bottom of the park well. The water-level data collected from the park well are compared to flow data on the South Fork of the Palouse River at the gage in Pullman because a discharge gaging station has not been established on Union Flat Creek. Figure 5-18 shows the proximity of the watersheds of Union Flat Creek and the South Fork of the Palouse River. This analysis is based on the assumption that the timing of flow events in Union Flat Creek would be similar to timing of events in the South Fork of the Palouse River.

5.6.2 Hydrograph Analysis for High Flow Events at the Klemgard Park Site Water levels in the Klemgard Park well reflect operation of the well for park activities including irrigation in the summer months (Figure 5-19). Ground-water levels are lower during the summer months of 2007 to 2009 because of pumping of the well. The water level in the well gradually recovers during the fall. The discharge of the South Fork of the Palouse River peaks in the winter and early spring related to precipitation and snowmelt events. Figure 5-19 shows a rapid response of ground-water levels in the Klemgard Park well to flow events in Union Flat Creek (as represented by the hydrograph from the South Fork of the Palouse River). The multiple high flow events that occurred in late 2008 and the first three months of 2009 are reflected in higher ground-water levels in the park well. Ground-water levels recede after the high flow events to the start of the summer season pumping. The aquifer penetrated by the Klemgard Park well appears to be hydraulically connected to Union Flat Creek as represented by the hydrograph of the South Fork of the Palouse River. According to Heinemann (1994), the well is completed in the uppermost basalt flow of the Grande Ronde Formation. It is unknown whether the aquifer penetrated by the park well is part of the lower aquifer as occurs in the eastern portion of the Palouse Basin.

5.7 Conclusions

A ground-water response to surface-water flood events was not discernable in the lower aquifer at the Pullman and Palouse sites or in the upper aquifer at the Moscow site. However, the well at Klemgard Park does show a hydraulic response to flood events in Union Flat Creek (as

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Palouse Ground Water Basin Framework Project FINAL report represented by flow data from the South Fork of the Palouse River). More detail relative to each of the study areas is given below.  The channel of the South Fork of the Palouse River is incised to near the contact between the Wanapum Formation and the underlying Grande Ronde Formation in downtown Pullman. However, wells completed in the lower aquifer show no discernable response to stream flood events.  A considerable thickness of basalt and sediment separates the base of the Palouse River from the lower aquifer where the City of Palouse wells are located. Wells completed in the lower aquifer hundreds of feet below the stream channel show no discernable water- level response to stream flood events. The water temperature data from Palouse well #3 can be explained by the placement of the data logger about 100 feet above the top of the lower aquifer.  Wells completed in the upper portion of the upper aquifer at the UI Groundwater Field Laboratory show a response to flow events in Paradise Creek. However, wells completed in the lower portion of the upper aquifer do not show water-level response to flood events in the creek.  The well at Klemgard Park shows a water-level response to flood events in Union Flat Creek (as represented by the hydrograph of the South Fork of the Palouse River). It is unknown whether the aquifer penetrated by the well represents the lower aquifer as defined for the Pullman-Moscow and northern subareas of the Palouse Basin.

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Chapter 5 Figures

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Figure 5-1 Map showing the working boundary for the Palouse Ground Water Basin and study sites for surface-water/ground-water interaction investigation.

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Figure 5-2 Comparison of Spokane River stage and water levels in selected wells completed in the Spokane Valley/Rathdrum Prairie Aquifer (Caldwell and Bowers, 2003).

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The USGS gauging station on the South Fork of the Palouse River is located immediately adjacent to Pullman well #1

The WSU test well is located in the same building as WSU well #1

South Fork of the Palouse River

Cornelius Well

Figure 5-3 Location map for the South Fork of the Palouse River at Pullman (Anderson et al., 2008).

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Figure 5-4 Cross sections for the South Fork of the Palouse River at Pullman (Anderson et al., 2008).

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Figure 5-5 Hydrographs for WSU test well and Pullman well #8 in comparison to the discharge record for the South Fork of the Palouse River at Pullman.

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Figure 5-6 Hydrograph for the Cornelius well comparison to the discharge record for the South Fork of the Palouse River at Pullman.

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Palouse Well #1

Palouse Well #3

Figure 5-7 Locations of wells and cross sections in the vicinity of the City of Palouse (Bush and Garwood, 2005f).

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Figure 5-8 Cross sections A-A’ and G-G’ in the vicinity of the City of Palouse (Bush and Garwood, 2005f).

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Figure 5-9 2007-2008 hydrograph for the City of Palouse wells in comparison to the discharge record for the Palouse River at Potlatch.

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Figure 5-10 2008-2009 hydrograph for the City of Palouse wells in comparison to the discharge record for the Palouse River at Potlatch.

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Figure 5-11 Winter water temperature data for City of Palouse wells (Gregory, personal communication, 2010).

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Figure 5-12 Summer water temperature data for City of Palouse Wells (Gregory, personal communication, 2010).

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USGS Gaging

Well INEL‐D

Figure 5-13 Moscow area location map (modified from Bush, 2006a).

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Figure 5-14 Geologic cross section through IDWR (Moscow) Well #4 (Bush, 2006a).

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Figure 5-15 Cross section through the INEL well (Kopp, 1994).

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Figure 5-16 2006-2009 hydrograph for the INEL-D and IDWR-3 wells in comparison to the discharge record for Paradise Creek at Moscow.

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Figure 5-17 Hydrograph for the INEL-D and IDWR-3 wells and discharge record for Paradise Creek at Moscow for the 2007- 2008 water year.

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Figure 5-18 Location map for Klemgard Park along Union Flat Creek (Gregory, personal communication, 2010).

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Klemgard Obs Well vs South Fork Palouse River 05/15/06 08/13/06 11/11/06 02/09/07 05/10/07 08/08/07 11/06/07 02/04/08 05/04/08 08/02/08 10/31/08 01/29/09 04/29/09 07/28/09 5 360

10 300

15 240

20 180

25 120 Depth to Water MP Water to Depth SFPR Dischrage in in cfs SFPR Dischrage

30 60

35 0 Klemgard Misc measurements SFPR Discharge

Figure 5-19 Hydrograph for the Klemgard Park well in comparison to the discharge record for the South Fork of the Palouse River at Pullman (Gregory, personal communication, 2010).

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Chapter 5 Tables

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Table 5-1 Well inventory for surface-water/ground-water interaction task Interval Open to Screened/Open TOC Ground Date Depth Aquifer Intervals Elevation Elevation Well Number Status Drilled Aquifer (ft) (ft bgs) (ft amsl) (ft amsl) (ft amsl) Reference(s) 329-369, 2187-2144, 409-489, 2104-2024, 519-539, 1994-1974, 559-579, 1954-1934, 584-714, 1929-1799, Pullman #8 -- 2007 GR 793 754-794 1759-1719 -- 2513 Anderson et al. (2008) PBAC 1999 Annual Report; Robischon, personal comm. Palouse #1 active 1910 GR 297 220-297 -- -- 2433 (2010) 2000- Palouse #3 active 1999 GR 438 400-435 ------PBAC 1999 Annual Report Cornelius monitor 1997 GR 245 -- -- 2455 -- PBAC records IDWR #2 monitor 2006 WP 282 -- -- 2625 -- Bush (2006); PBAC records IDWR #3 monitor 2006 WP 355 -- -- 2626 -- Bush (2006); PBAC records IDWR #4 monitor 2006 GR 735 -- -- 2624 -- Bush (2006); PBAC records INEL Deep monitor 1992 WP 205+ -- 192-202+ 2548 2545+ PBAC records; Kopp (1994) PBAC 1999 Annual Report; WSU test monitor -- GR 144 144 2220 -- 2364 Anderson et al. (2008) Klemgard Gregory (personal Park Active 1976 GR 150 130-150 communication, 2010) Notes: NA stands for not available or not applicable ft amsl stands for feet above mean sea level ft bgs stands for feet below ground surface (depth) TOC stands for top of casing GR stands for Grande Ronde WP stands for Wanapum

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Section 6.0 Task 4 – Data-Gap Investigation

6.1 Introduction

A large body of knowledge has been accumulated relative to the hydrogeology of the Palouse Ground Water Basin, particularly the Pullman-Moscow subarea. Three hundred and thirty-nine (339) documents including maps, cross sections, reports, presentations, etc., were reviewed as part of the Compilation and Synthesis tasks of the Palouse Ground Water Framework Project. These documents provide a great deal of information but do not necessarily provide the basis to respond to a number of important hydrogeologic questions, particularly those related to long- term water supply. One of the objectives of the Palouse Basin Framework Study is to conduct a data gap analysis relative to ground-water resources. This chapter of the report includes delineation of a prioritized list of data gaps and provides guidance relative to investigation programs needed to satisfy the high and medium priority information needs. Data gaps associated with surface water, including water sources for aquifer storage and recovery projects, are not addressed in this chapter. The results from preliminary analysis of two data gaps identified early in the Framework Project are presented in Sections 4 and 5 of this report.

6.2 Delineation of Data Gaps

The criteria used to delineate and prioritize data gaps for this analysis are listed below. First, the data gap must be directly related to long-term utilization of ground water as a water- supply source, with particular emphasis on the Pullman-Moscow subarea.  Ground water is the primary water supply source for residents of the Palouse Basin. This includes municipalities, universities, and a variety of smaller water users. Thus, data gaps directly related to long-term water supply are of primary importance.  The historical problems of water-level decline within the Palouse Basin have been limited primarily to the Pullman-Moscow subarea with some decline also occurring in the City of Palouse wells in the northern subarea. Thus, the data gap focus is on the Pullman- Moscow subarea with limited emphasis on the northern subarea. Second, the data gap must be defined such that a successful investigational program can be conducted.  A number of data gaps exist that cannot be successfully addressed with an investigational program. Determination of the amount of recharge to the lower aquifer is an example of a data gap which cannot be determined by a field study. The primary mechanism for recharge to the lower aquifer is downward leakage from the upper aquifer which in turn is controlled by vertical hydraulic conductivity. Field determination of vertical hydraulic conductivity over a large area is a near-impossible task.  An identified data gap must have an associated investigational program that has a reasonable probability of success.  The program must be able to be conducted in a reasonable period of time and at a reasonable cost.

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Potential data gaps related to water supply were identified, evaluated with respect to the above described criteria, and then prioritized. They are listed below under the headings high, medium, and low priority. Subsequent sections of this chapter provide guidance relative to investigation programs needed to satisfy the high and medium priority data gaps.

6.2.1 High-Priority Data Gaps

6.2.1.1 Hydrogeology West of Pullman The hydraulic characteristics of the lower aquifer along the west side of the Pullman-Moscow subarea are poorly understood. A number of investigators have concluded that the complex geology along a northwest trending band west of Pullman has created a zone of lower hydraulic conductivity which acts to “dam” water within the lower aquifer east of the zone. Barker (1979) postulated the presence of a “barrier zone” to explain the spatial and temporal patterns of water levels in the lower aquifer in the Pullman and Moscow area. Improved knowledge of the “barrier zone” is important because this zone controls ground-water outflow from the Pullman- Moscow subarea. The zone may serve to isolate areas to the west from impacts from pumpage in Pullman-Moscow area. Construction of production wells west of the “barrier zone” may be a viable alternative for water supply development for WSU and Pullman.

6.2.1.2 Surface-Water / Ground-Water Interaction Northwest of Pullman Stream gain-loss information collected by the Washington Department of Ecology on the South Fork of the Palouse River indicates an area of stream loss in a reach a short distance northwest of downtown Pullman (Sinclair and Kardouni, 2009). Barker (1979) in his numerical model utilized vertical leakage along the valley of the South Fork of the Palouse River from Pullman to Albion as part of his representation of the lower aquifer water-resource system. This hydraulic connection between the South Fork and the upper and/or lower aquifers, if it exists, is important to present use of the aquifers and may represent an area for recharge activities for the lower aquifer.

6.2.1.3 Maximizing Upper-Aquifer Pumping in the Pullman-Moscow Subarea Gaining a greater understanding of the maximum yield potential of the upper aquifer in the Pullman-Moscow subarea is important to water supply issues within the Basin. Possibly, a greater portion of the water production for Moscow can be obtained from the upper aquifer, particularly from new wells located near the state line. New development along the east side of Pullman possibly can be supplied with water from the upper aquifer. This data gap includes consideration of both water-quantity and water-quality issues.

6.2.2 Medium-Priority Data Gaps

6.2.2.1 Ground-Water Monitoring Program The mass water-level measurements obtained in 1974 as part of the Barker (1979) study and in 1985 as part of the Lum et al. (1990) study have provided important information relative to water-level decline patterns in the Palouse Basin, particularly the Pullman-Moscow subarea. Such a program is needed on a 10-year frequency throughout the Palouse Basin to provide the basis of interpreting impacts from pumpage and water management activities. The program would involve establishment of a network of wells in both the upper and lower aquifers,

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6.2.2.2 Lower-Aquifer Continuity in the Kamiak Butte to Angel Butte Gap The continuity and characteristics of the lower aquifer from the Pullman-Moscow subarea through the bedrock gap between Kamiak Butte and Angel Butte to the city of Palouse in the northern subarea is poorly understood. Improved knowledge in the vicinity of the gap would be useful in assessing the boundaries of the lower aquifer and aid in any future numerical ground- water models of the system.

6.2.2.3 Hydraulic Sub-basins Within the Pullman-Moscow Subarea Most investigators have concluded that the lower aquifer acts a single system within the Pullman-Moscow subarea over long time periods of time. The long-term rates of water-level decline are similar throughout the subarea as are the static water-level elevations. However, recent research suggests that portions of the aquifer act as leaky separate blocks over time periods of weeks to months. Improved knowledge of potential hydraulic sub-basins within the Pullman-Moscow subarea would be useful for analysis of management alternatives, particularly if use of surface water via aquifer storage and recovery programs is considered as a management alternative.

6.2.2.4 Relationship Between Pumping and Water-Level Decline An analysis of the temporal relationship between annual water withdrawal and the average annual rate of water-level decline would provide important information relative to the characteristics of the lower aquifer in the Pullman-Moscow subarea. The annual water withdrawal calculated per foot of water-level decline, taken over the areal extent of the aquifer within the subarea, allows estimation of the long-term storativity of the aquifer. Temporal changes in the annual withdrawal per foot of decline potentially can be used to learn about changes in recharge and/or discharge rates caused by the water-level decline.

6.2.2.5 Well-Log Database Assembling all of the well logs for wells within the Palouse Basin and entering the data into a geospatial database was initially part of the Palouse Ground Water Basin Framework Project. However, the scope of work changed and much of this work remains. This project would allow researchers quick access to well logs and well data that may have otherwise been difficult to find.

6.2.3 Low-Priority Data Gaps

6.2.3.1 Ground-Water Conditions in the Colton, Uniontown, and Genesee Areas Both of the numerical ground-water models of the Palouse Basin (Barker, 1979; Lum et al., 1990) included ground-water flow into the Pullman-Moscow subarea from the south around the west end of the bedrock high that is located near Johnson, Washington. The water supplies for Colton and Uniontown in Washington and Genesee in Idaho are derived from the upper aquifer.

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The presence or absence of the lower aquifer in these areas is unknown. This project would focus on the hydrogeology of the area that includes Colton, Uniontown, and Genesee.

6.2.3.2 Ground-Water Conditions in the Garfield Area Garfield is located near the northern boundary of the Palouse Basin as currently defined. Available information indicates that the city is underlain by two aquifers that may be equivalent to the upper and lower aquifers as identified within the Pullman-Moscow subarea. Additional investigation is needed in the Garfield area to determine whether the Garfield area is underlain by a lower aquifer that is hydraulically connected to the lower aquifer under the city of Palouse. The study would also include identification of wells that can be included in the mass water-level measurement program identified above.

6.2.3.3 Ground-Water Conditions in the Colfax Area The Colfax area has not been the subject of detailed ground-water investigations, primarily because problems of declining ground-water levels have not been identified. Additional investigation in the Colfax area would be focused on the geologic controls for the flowing artesian Glenwood wells and on the identification of wells that can be included in the mass water-level measurement program described above.

6.2.3.4 Surface-Water / Ground-Water Interaction Near Colfax The WDOE 2009 study identified several areas of significant stream loss in the Palouse River and the South Fork of the Palouse River in the general vicinity of Colfax (Sinclair and Kardouni, 2009). Additional investigation is needed to gain a better understanding of the geologic and hydrogeologic controls for these stream loss reaches. This knowledge would be useful understanding the recharge-discharge characteristics of the Basin.

6.3 Details of High-Priority Data Gaps

6.3.1 Hydrogeology West of Pullman Gaining an improved understanding of the hydrogeology in the area between Pullman and Union Flat Creek is a high priority. Available information indicates that this area exerts an important influence on ground water in the Pullman-Moscow area. Authors of both Palouse Basin numerical models (Barker, 1979; and Lum et al., 1990) had difficulty representing this portion of the Basin.

6.3.1.1 Purpose and Objective The purpose of this proposed project is to investigate the hydrogeologic characteristics of subsurface in the area west of Pullman that Barker (1979) postulated to be a “barrier zone” (Figure 6-1). The general objective of the proposed project is to characterize the subsurface geology and hydrogeology in the upper and lower aquifers in a study area located southwest of Pullman based on data collected from the construction of several monitor wells coupled with data from existing wells.

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6.3.1.2 Proposed Project Location Several criteria were used in selection of the proposed project area where the investigation would take place. First, the area should be within the “barrier zone” as postulated by Barker (1979) (Figure 6-1). Second, the project area should be oriented northeast-southwest to be at approximate right angle to the alignment of the postulated “barrier zone.” Third, the area should be located where existing wells provide some geologic control and the opportunity for water- level data collection. Fourth, to the extent possible, the area should include county roads to facilitate the construction of monitor wells on publically owned land. Fifth, the project area should be located close enough to Pullman to facilitate analysis of pumping impacts within or across the “barrier zone” from operation of Pullman and WSU production wells. The proposed project area is located southwest of Pullman and extends from Pullman to Union Flat Creek (Figure 6-2). The area contains a number of county roads including Country Club Road and Wawawai–Pullman Road. Key to the selection of this area is the presence of two deep wells (14N/44E-14P01 and 14P02) located at the WSU Knott Dairy Farm located along Country Club Road. These wells are believed to be completed in the lower aquifer. The wells have similar water-level elevations to wells completed in the lower aquifer in Pullman but do not have the same pattern of long-term water-level decline as is evident in Pullman. Figure 6-3 shows that a limited number of water-level measurements for well #1 in the period from 1959 to 1990 show a rate of decline of slightly more than 2 feet per year. Air-line water-level data from 2004 to 2010 show essentially no decline in either of the wells. The lack of apparent water-level decline in the WSU Dairy Farm wells in recent years makes this an important location for additional hydrogeologic investigations.

6.3.1.3 Project Description The project would be conducted in the following steps.  Existing geologic and hydrogeologic data would be analyzed and used to select locations and designs for the new monitor wells. The new wells should be constructed to penetrate down to and be completed in the upper portion of the lower aquifer. o Geologic data from existing wells and published geologic maps and cross sections would be used to develop a geologic conceptual model of the study area. The focus would be on identification of structural features. o Water-level data from existing wells along with the geologic information would be used to develop a hydrogeologic conceptual model of the study area. o Topographic maps plus the structural map of the top of the Grande Ronde Formation (Bush and Garwood, 2005j) would be used to estimate the required well depths at alternative well sites. o The above information plus an analysis of land availability would be used to select target monitor well locations. o Well designs and drilling plans would be developed based on the geologic and hydrogeologic conceptual models plus the selected well locations.  Two to four monitor wells would be constructed in a single construction program. o The well construction program would be designed to maximize on-site collection of geologic and hydrogeologic information. . Laboratory chemical analysis would be conducted on drill cuttings. . Water levels and yield information would be measured during drilling.

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o Information gained from construction of the first well would be used to guide location, design, and construction of subsequent wells. o Example well locations are shown on Figure 6-4. The target depth of each well depends on the elevation of the drill site selected and the elevation of the top of the lower aquifer (assumed to be within 100 feet below the top of the Grande Ronde Formation). Based on the work by Bush and Garwood (2005j), the top of the Grande Ronde Formation dips about 50 feet to 60 feet per mile to the southwest in the vicinity of the proposed project. Construction of the monitor wells within stream valleys would minimize the required depth because of lower surface elevations. . The target depth of example monitor well A in the Wilber Creek Valley would be about 490 feet (land elevation of about 2,480 feet minus top of Grande Ronde Formation at about 2,090 feet plus penetration into the Grande Ronde Formation of about 100 feet). . The target depth of example monitor well B, drilled in the valley of Union Flat Creek, would be about 420 feet (land elevation of about 2,320 feet minus top of Grande Ronde Formation at about 2,000 feet plus penetration into the Grande Ronde Formation of about 100 feet). . Wells drilled in the valleys further to the west would tend to be shallower because the land elevation is lower, with little predicted change in the elevation of the top of the Grande Ronde Formation. o The elevation and location of each of the monitor wells would be surveyed. o A stratigraphic description of each well would be created based on data collected during construction including visual inspection and chemical analysis of the cutting samples. o Water-level and yield information, collected during well construction, would be used to describe the hydrogeologic units for each monitor well.  The geologic and hydrogeologic information gained from the construction of the monitor wells coupled with existing subsurface information would be used to formulate revised conceptual geologic and hydrogeologic models of this portion of the Palouse Basin. o Maps and geologic cross sections would be developed. o Hydraulic gradients, both horizontally within a given hydrogeologic unit and vertically between units, would be calculated. o A conceptual model of the “barrier zone” and the role the zone plays in controlling ground-water flow within the Grande Ronde aquifer would be developed.  A program of temporal water-level measurements in the constructed monitor wells and selected existing wells would be initiated.

6.3.1.4 Project Cost Estimate The dominant cost item for the proposed project is the construction of monitor wells. A general estimate of well construction costs is presented below based on construction costs for the Idaho Department of Water Resources (IDWR) monitor wells drilled north of the Palouse Empire Mall in Moscow in 2006 (Ralston, personal communication, 2010) plus cost information obtained from Tom Richardson of H2O Well Services (personal communication, September 2, 2010).

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 Four wells were constructed for the IDWR project. The charge for mobilization and site preparation for the project was $26,500. The price per foot for constructing the three deeper wells was as follows: $106 per foot for the 282-foot well, $147 per foot for the 355-foot well, and $197 per foot for the 750-foot well. In all cases, the wells were constructed with 4-inch diameter PVC casing. The cost of construction of the IDWR wells was higher than what might be expected at the project site southwest of Pullman because of the presence of thick sedimentary interbeds at the Moscow site. The IDWR wells were constructed using a combination of mud rotary and air rotary drilling techniques. The project site southwest of Pullman is underlain mostly by basalt. Likely, the monitor wells could be constructed using only air rotary techniques.  Tom Richardson of H2O Well Services provided the following cost estimates for wells drilled using only an air rotary rig: $30 per foot for drilling 8-inch diameter open hole, $22 per foot for installation and removal of temporary 8-inch diameter casing (if needed), and $30 per foot to install 4-inch diameter PVC casing and screen with sand around the screen and seal material in the annular space to land surface. Site preparation of mobilization costs would be additional to those given above. An estimate of $100 per foot based on information from Tom Richardson is used to develop the following cost estimate. The estimated project costs for the project if two monitor wells are drilled is approximately $170,000. This includes $70,000 for professional services and drilling costs of about $100,000 (including mobilization) for two monitor wells with a combined depth of about 1,000 feet. The drilling costs would be about 25 percent less if the completion casing is 2 inches in diameter rather than 4 inches in diameter.

6.3.2 Surface-Water / Ground-Water Interaction Northwest of Pullman The stream loss identified by WDOE (Sinclair and Kardouni, 2009) on the South Fork of the Palouse River a short distance northwest of Pullman indicates that the stream recharges the upper aquifer and possibly the lower aquifer in this area (Figure 6-5). The approximate reach where the maximum stream loss was detected is between stream stations AKY492 and AKY490 (Figure 6-6). The hydraulic connection between the South Fork of the Palouse River and ground-water systems in the reach immediately northwest of Pullman is of considerable importance to the Basin.

6.3.2.1 Purpose and Objectives The purpose of this proposed project is to gain an improved understanding of the hydrogeologic characteristics in the area of a losing reach of the South Fork northwest of Pullman. Sinclair and Kardouni (2009) identified the stream reach where the loss occurred and documented water-level responses in a shallow well in the area (site AGJ768 on Figure 6-6). The general objective of the proposed project is to characterize the subsurface geology and hydrogeology in the upper and lower aquifers in a study area located northwest of Pullman based on data collected from the construction of two or more monitor wells coupled with data from existing wells. A primary focus of the study is to determine if the stream-loss area is coincident with structural features such as folds in the underlying basalt units.

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6.3.2.2 Proposed Project Location The project area is located along the identified losing reach of the South Fork northwest of Pullman (from AKY492 to AKY490 on Figure 6-6). Most of the work would be conducted within the valley.

6.3.2.3 Project Description The project would be conducted in the following steps.  Existing geologic and hydrogeologic data would be analyzed and used to develop geologic and hydrogeologic conceptual models. o Geologic data from existing wells and published geologic maps and cross sections would be used to develop a geologic conceptual model of the study area. The focus would be on identification of structural features. o Water-level data from existing wells along with the geologic information would be used to develop a hydrogeologic conceptual model of the study area. o Topographic maps plus the structural map of the top of the Grande Ronde Formation (Bush and Garwood, 2005j) would be used to estimate the required well depths to reach the Grande Ronde Formation at alternative well sites.  The locations and designs for two or more monitor wells would be developed. The new wells should be constructed to penetrate down to and be completed in the upper portion of the lower aquifer. o The conceptual models described above coupled with the stream loss data and information on land availability would be used to select target monitor well locations. o Well designs and drilling plans would be developed based on the geologic and hydrogeologic conceptual models plus the selected well locations.  Two or more monitor wells would be constructed in a single construction program. o The well construction program would be designed to maximize on-site collection of geologic and hydrogeologic information. . Laboratory chemical analysis would be conducted on drill cuttings. . Water levels and yield information would be measured during drilling. o Information gained from construction of the first well would be used to guide location, design, and construction of the second and succeeding wells. o The wells would be constructed in the South Fork valley to minimize construction costs. o The elevation and location of each of the monitor wells would be surveyed. o A stratigraphic description of each well would be created based on data collected during construction including visual inspection and chemical analysis of the cutting samples. o Water-level and yield information, collected during well construction, would be used to describe the hydrogeologic units for each monitor well.  The geologic and hydrogeologic information gained from the construction of the monitor wells coupled with existing subsurface information would be used to formulate revised conceptual geologic and hydrogeology models of this portion of the Palouse Basin. o Maps and geologic cross sections would be developed.

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o Hydraulic gradients, both horizontally within each hydrogeologic unit and vertically between units, would be calculated. o A conceptual model of the subsurface conditions underlying the losing reach of the South Fork would be developed.  A program of temporal water-level measurements and water quality sampling would be initiated in the constructed monitor wells and selected existing wells. o Data loggers would be installed in the monitor wells and selected existing wells. The ultimate use of the water-level data would be to analyze responses to pumping of Pullman and WSU production wells and to identify any response to flood events within the South Fork. o Water samples would be collected from the monitoring wells and selected private wells and analyzed for common ions plus those constituents that might serve as tracers related to recharge from the South Fork.

6.3.2.4 Project Cost Estimate The costs for the proposed project would be a combination of well construction costs plus professional services costs. The target depth of each well depends on the elevation of the drill sites selected and the elevation of the top of the lower aquifer. Based on the work by Bush and Garwood (2005), the top of the Grande Ronde Formation is present at a depth of less than 50 feet under the valley floor within the proposed study site (Figure 6-7). The depth of monitor wells at any site within the valley floor would be about 200 feet (depth to the top of the Grande Ronde Formation plus penetration into the formation). The estimated costs for the described project are approximately $120,000. This includes $80,000 for professional services and expenses coupled with drilling costs of $40,000 for two monitor wells with a combined depth of about 400 feet.

6.3.3 Maximizing Upper Aquifer Pumping in the Pullman-Moscow Subarea The upper aquifer was the sole water supply source for Moscow and UI until the 1960s when wells were completed in the lower aquifer. Water levels in Moscow, which had declined by about 100 feet by the 1960s, recovered when withdrawal was switched to the lower aquifer. Moscow currently produces 19 percent to 36 percent of its supply from the upper aquifer via wells #2 and #3 (Robischon, personal communication, 2010). The historical pattern of water- level decline followed by recovery that occurred in the Moscow area does not appear to have extended to the Pullman area.

6.3.3.1 Purpose and Objectives The purpose of this proposed project is to gain an improved understanding of the hydrogeologic characteristics and water balance for the upper aquifer in the Pullman-Moscow subarea. The general objectives of the proposed project are as follows: 1) to characterize the hydraulic characteristics and water quality in the upper aquifer within the Pullman-Moscow subarea with an emphasis on the area of the Moscow-Pullman corridor, and 2) to determine the feasibility and expected consequences of increasing water production from the upper aquifer in the western side of Moscow and/or the eastern side of Pullman.

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6.3.3.2 Proposed Project Location The proposed project location is in the Moscow-Pullman corridor (Figure 6-8).

6.3.3.3 Project Description The project would be conducted in the following steps.  Existing geologic and hydrogeologic data would be analyzed and used to develop geologic and hydrogeologic conceptual models of the upper aquifer between Moscow and Pullman. o The geologic analysis would focus on the continuity of basalt and sediment units between the two cities. o The hydrologic analysis would focus on three topics: 1) the hydraulic continuity of water-producing zones in basalt and sediment in the area between the two cities, 2) the historical water-level changes in the area between the two cities, and 3) the water quality in the upper aquifer at various locations in the study area.  A numerical model of the upper aquifer within the Pullman-Moscow subarea would be developed, likely as a student thesis project at one of the universities. o The model would be constructed using existing information and calibrated using historical pumpage and water-level data. o The objective of the model would be to assess the impacts associated with increased water withdrawal at selected locations in the Moscow-Pullman subarea.  Water management alternatives evaluated using the numerical model would include the following. o Model simulation would include operation of upper aquifer wells in the western side of Moscow, possibly near the locations of Moscow well #9 and planned Moscow well #10. Construction of wells into the upper aquifer near wells completed in the lower aquifer would allow the use of existing or planned piping plus the opportunity to mix water from the two aquifers in such a way as to mitigate any water quality issues associated with water from the shallow aquifer. o Additional model simulation would include operation of upper aquifer wells in the area from the state line to the Pullman city limits. These wells could represent water-supply sources for the area likely for future growth in the Pullman-Moscow corridor. o The model could also be used to evaluate the impacts associated with possible aquifer storage and recovery operations within the upper aquifer in the area of interest.

6.3.3.4 Project Cost Estimate The costs for the proposed project would depend on whether the work described is carried out as a university research effort or conducted by private-sector organizations. The cost for the three tasks described above likely would be $50,000 to $100,000.

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6.4 Details of Medium-Priority Data Gaps

6.4.1 Ground-Water Monitoring Program Measurements of water levels in a number of wells at about the same period of time are used in other basins to provide a snapshot of conditions within the ground-water system. In the case of the Palouse Basin, such mass water-level measurements were taken in 1974 and 1985 by the USGS as part of the Barker (1979) and Lum et al. (1990) numerical model studies. The focus of this proposed project is to develop a network of wells to be used for ground-water monitoring including a program of mass measurement of ground-water levels in the Palouse Basin.

6.4.1.1 Purpose and Objectives The purpose of this proposed project is to establish a network of wells throughout the Palouse Basin and completed in either the upper or lower aquifers to use in a water-level monitoring program including a mass measurement tentatively scheduled for 10-year intervals. The general objective is to establish a network of wells located throughout the Basin that can be measured (via access tubes in most cases) when needed (long-term access agreements would be needed). The additional sites would be added to the network of wells operated and measured by PBAC members and the limited number of publically owned monitor wells that are in place. The focus would be to add wells in the network that are outside of the immediate vicinity of Pullman and Moscow.

6.4.1.2 Proposed Project Location The project area includes the Palouse Basin and presently delineated areas plus adjacent areas as deemed important (e.g., Colton, Uniontown, Genesee, and Potlatch).

6.4.1.3 Project Description The project would be conducted in the following steps.  Each subarea of the Palouse Basin would be examined relative to the location and completion aquifer of wells operated and measured by PBAC members and the limited number of publically owned monitor wells. Target areas for additional wells would be away from the above identified wells.  Wells with historical water-level measurements would be reviewed from the USGS website with the focus on the target areas within each subarea.  Well log files from IDWR and WDOE would be reviewed with the focus of identifying wells within the target areas in each subarea.  A list of potential wells for inclusion into the monitoring network would be developed.  Owners of the wells would be contacted and site visits would be arranged.  The site visits would include collection of information on the well and measurement of depth to water if possible.  The following procedures would be followed for wells selected for inclusion in the network. o Access tubes would be installed in any wells where pumps have been installed. o Long-term legal access agreements would be obtained for all wells.  A report providing information on the well network would be prepared.

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6.4.1.4 Project Cost Estimate The costs for the proposed project would depend on whether the work described is done in the private sector or whether it is operated as a university research effort or conducted by PBAC staff. The cost for the tasks described above likely would be $50,000 if conducted in the private sector but would be much less as a university research effort or conducted by PBAC staff.

6.4.2 Lower-Aquifer Continuity in the Kamiak Butte to Angel Butte Gap Geophysical studies and short-term aquifer tests have provided inconclusive or conflicting evidence for the continuity of the lower aquifer between the northern subarea and the Pullman- Moscow subarea. This area is the gap between crystalline bedrock highs of Kamiak Butte and Angel Butte. Improved geologic and hydrogeologic understanding of the gap would be useful in assessing the boundaries of the lower aquifer and aid in any future numerical ground-water models of the system.

6.4.2.1 Purpose and Objectives The purpose of this proposed project is to gain an improved understanding of the lower aquifer connection between the northern subarea and the Pullman-Moscow subarea. The general objectives of the proposed project are as follows: 1) determine if the Grande Ronde Formation exists in the gap, and 2) if it does exist, develop information on the lower aquifer in this area.

6.4.2.2 Proposed Project Location The proposed project location is in the Kamiak Butte to Angel Butte gap (Figure 6-9).

6.4.2.3 Project Description The project would be conducted in the following steps.  Existing geologic, geophysical, and hydrogeologic data would be analyzed and used to develop a conceptual model of the bedrock gap area.  The locations and designs for most likely one monitor well would be developed in the Kamiak Butte to Angel Butte gap area (Figure 6-9). The purpose of the monitoring well is to determine if the Grande Ronde Formation exists in the study area. The new well should be constructed to penetrate down to and be completed in the upper portion of the lower aquifer, if present. o The conceptual models and information on land availability would be used to select target monitor well locations. o Well designs and drilling plans would be developed based on the geologic and hydrogeologic conceptual models plus the selected well location.  Likely one monitor well would be installed. o The well construction program would be designed to maximize on-site collection of geologic and hydrogeologic information. . Laboratory chemical analysis would be conducted on drill cuttings. . Water levels and yield information would be measured during drilling. o Information gained from construction of the first well would be used to guide location, design, and construction of a second well, if needed.

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o The elevation and location of the monitor well would be surveyed. o A stratigraphic description of the well would be created based on data collected during construction including visual inspection and chemical analysis of the cutting samples. o Water-level and yield information, collected during well construction, would be used to describe the hydrogeologic units for the monitor well.  The geologic and hydrogeologic information gained from the construction of the monitor well coupled with existing subsurface information would be used to formulate revised conceptual geologic and hydrogeology models of this portion of the Palouse Basin. o Maps and geologic cross sections would be developed. o The hydraulic gradients, both horizontally within a given hydrogeologic unit and vertically between units, would be calculated. o A conceptual model of the subsurface conditions in the gap would be developed.

6.4.2.4 Project Cost Estimate The costs for the drilling the monitoring well would be a combination of well construction costs plus professional services costs. The target depth of each well depends on the elevation of the drill site selected and the elevation of the top of the lower aquifer (assumed to be 100–300 feet below land surface). The estimated depth of the monitor well is about 300 feet. The estimated cost for well installation and professional services is approximately $45,000. This includes $15,000 for professional services and expenses coupled with drilling costs of $30,000 for one monitor well with a depth of about 300 feet.

6.4.3 Hydraulic Sub-Basins Within the Pullman-Moscow Subarea Currently, a long-term lower aquifer test is being conducted to delineate annualized effective aquifer system storativity and water-level responses in the Palouse Basin. Early findings of this work indicate the presence of short-term, hydraulic sub-basins within the Pullman-Moscow subarea. Improved knowledge of potential aquifer compartmentalization within the Pullman- Moscow subarea would be useful for analysis of management alternatives, particularly if aquifer and recovery programs are considered as a management alternative. A continuation of the project is proposed and was presented by Dr. Jim Osiensky of the University of Idaho at the August 19, 2010 PBAC meeting.

6.4.3.1 Purpose and Objective The purpose of this project is to improve the understanding of potential hydraulic sub-basins within the Pullman-Moscow subarea. The general objective of the proposed project is to continue operation and analysis of a long-term aquifer stress test to delineate annualized water- level responses and thus to evaluate potential aquifer compartmentalization.

6.4.3.2 Proposed Project Location The proposed project location is within the Pullman-Moscow subarea.

6.4.3.3 Project Description The project description, titled “Project Scope of Work – Continuation of Long-Term Grande Ronde Aquifer Stress Testing to Delineate Annualized Effective Aquifer System Storativity and

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Water-Level Responses in the Palouse Basin,” was outlined by Dr. Jim Osiensky at the August 19, 2010 PBAC meeting. Details can be provided by Dr. Osiensky.

6.4.3.4 Project Cost Estimate Dr. Osiensky provided a project budget of $50,375.

6.4.4 Relationship Between Pumping and Water-Level Decline Withdrawal of water from the lower aquifer since the 1890s has resulted in a pattern of long-term water-level decline. The rate of water-level decline in any ground-water system may not be directly proportional to the rate of pumping because of a number of Basin factors. The factors include: 1) the degree to which recharge can be increased by water-level decline, 2) the degree to which discharge from the aquifer is decreased because of the water-level decline, and 3) the degree to which aquifer parameters vary.

6.4.4.1 Purpose and Objectives The purpose of this project is to analyze the relationship between pumping and water-level decline in the lower aquifer in the Pullman-Moscow subarea of the Palouse Basin. In addition, the annual withdrawal per foot of water level decline, taken over the areal extent of the aquifer within the subarea, allows estimation of the long-term basin-wide storativity of the aquifer.

6.4.4.2 Proposed Project Location The project area is the Pullman-Moscow subarea of the Palouse Basin.

6.4.4.3 Project Description The project would be conducted in the following steps.  The hydrographs for wells completed in the lower aquifer that have long-term records would be reviewed and an average rate of water decline per year would be determined for the Pullman-Moscow subarea.  A summary of total pumpage from the lower aquifer within the Pullman-Moscow subarea per year would be determined for the entire period of record, to the extent possible.  A graph that shows plots of annual water withdrawal and annual rate of water-level decline would be prepared for the entire period of record, to the extent possible. A second graph would be prepared that shows the temporal change of the ratio of annual pumping divided by annual rate of decline divided by plan view area of the aquifer in the Pullman-Moscow subarea. The second plot provides an estimate of the temporal change in long-term storativity of the aquifer.  A report would be prepared that provides the results of the study.

6.4.4.4 Project Cost Estimate The costs for the proposed project would be about $10,000 in professional services. Alternatively, the project could be conducted by PBAC staff.

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6.4.5 Well-Log Database As part of the initial Scope of Work for the Palouse Ground Water Basin Framework Project, a well-log databank was to have been created. This task was not completed due to budget cuts and a change in scope. This project is therefore classified as a data gap. The well log databank would contain well construction information in a geospatial database. Some of the well logs can be easily found or have been found on the WDOE and IDWR websites, although these have not been validated for association with the provided well data. Well logs from older wells (i.e., pre 1960s) would not be in the state agency databases and must be found by other means (e.g., well data in reports).

6.4.5.1 Purpose and Objectives The purpose of this project is to create a well information databank for researchers to use in geologic and hydrogeologic studies. The general objectives of the proposed project are as follows: 1) to assemble all of the well logs of wells in the Basin, 2) to enter pertinent well data into a geodatabase, and 3) to rectify digitized maps of well locations and create a geodatabase which includes point locations of the wells and other relevant data.

6.4.5.2 Proposed Project Location The proposed project location would be the entire Palouse Basin as currently defined by PBAC and an outside 5-mile buffer where the aquifer boundaries are not defined by contacts with crystalline rock.

6.4.5.3 Project Description The project would be conducted in the following steps.  Some of the well logs and associated well data have been downloaded from the WDOE and IDWR websites as part of the Framework Project. The remaining well logs would be downloaded. All of the well logs would need to be verified against the well data information, as these often do not correspond. The well construction data as acquired should be put into a single database.  Well logs in the PBAC files would be examined to determine which well logs have not been in the database. Well logs that are not currently in possession would be scanned and the data entered into the well database.  A search would be conducted in the Framework Project report database for reports containing well construction information. Well data in the reports would be entered into the well database.  A key field would be created within the well-information table to enable linking to spatial locations in the well feature class of the geodatabase. The joined well information can be used for analyses and for producing support maps.  The digitized maps would be rectified and a GIS layer would be created for well locations that were collected during the Compilation task.

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6.4.5.4 Project Cost Estimate The costs for the proposed project would depend on whether the work described is done in the private sector, conducted by PBAC, or conducted by one of the universities. The project could easily be broken into parts and conducted as funding is available and by different entities as well. The cost for the four tasks described above could range from $6,000 to $23,000 depending on the entity doing the work.

6.5 Summary and Conclusions

A synthesis of the geologic and hydrogeologic work conducted in the Palouse Basin is discussed in Section 3 of this report. As a result, a number of data gaps have been identified. The hydrogeologic data gaps listed in this report meet two criteria:  The data gap must be directly related to long-term utilization of ground water as a water supply source.  The data gap must be defined such that the investigational program has a reasonable chance of success. The data gaps are classified by priority as high, medium, and low. Details are provided relative to the investigation of the high and medium priority data gaps. The identified data gaps are listed below.  High-priority data gaps: o The hydrogeology west of Pullman. o Surface-water / ground-water interaction northwest of Pullman. o Maximizing upper-aquifer pumping in the Pullman-Moscow subarea.  Medium-priority data gaps: o A ground-water monitoring program. o Lower-aquifer continuity in the Kamiak Butte to Angel Butte gap. o Hydraulic sub-basins within the Pullman-Moscow subarea. o Relationship between pumping and water-level decline. o Create a well-log database.  Low-priority data gaps: o Ground-water conditions in the Colton, Uniontown, and Genesee areas. o Ground-water conditions in the Garfield area. o Ground-water conditions in the Colfax area. o Surface-water / ground-water interaction northeast of Colfax. The first two of the three high-priority data gaps should be the first studies conducted. In both of these suggested studies, drilling additional monitor wells is a main part of the project. Constructing new monitor wells is an essential aspect of improving hydrogeologic knowledge of

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Palouse Ground Water Basin Framework Project FINAL report the Palouse Basin. Both of these projects have the potential to identify water supply development or enhancement opportunities.  The hydraulic characteristics of the “barrier zone” may allow construction of new production wells in the lower aquifer west of Pullman with minimal impact on the lower aquifer within the Pullman-Moscow subarea. Switching water production from wells within the subarea to wells outside of the subarea has the potential to stabilize ground- water levels in the lower aquifer within the Pullman-Moscow subarea. Obviously, studies would have to be conducted to determine the water-producing characteristics of the area west of the “barrier zone.”  The hydraulic connection between the South Fork of the Palouse River and the upper and/or lower aquifers in the reach west of Pullman may provide the opportunity to enhance recharge to one or both of these units. The enhanced recharge may be accomplished by using short canals to spread water over more of the flood plain during high flow events. A number of water-quality and water-quantity issues are raised by this conjunctive management approach for surface water and ground water in this area.  The third high priority data gap would evaluate transferring a greater portion of the withdrawal in the Moscow and Pullman areas to the upper aquifer and thus reducing the water withdrawal from the lower aquifer. The key questions relate to the maximum yield that can be obtained from the upper aquifer without causing unacceptable rates of water- level decline. Water quality issues related to use of water from the upper aquifer are also important.

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Chapter 6 Figures

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Figure 6-1 Barrier zone within the lower aquifer as postulated by Barker (1979).

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Figure 6-2 Map showing the proposed study site for the investigation of the Pullman area hydrogeology.

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200

220 Well #1 Well #2 240

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Depth to water in feet 300

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1959 1969 1979 1989 1999 2009 2019

Figure 6-3 Depth to water data for WSU Knot Dairy Farm wells.

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Wilber Creek Vll

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WSU Knot Dairy Farm Wells 14N/44E‐14P01 and Union Flat Creek 14P02 ll

Figure 6-4 Possible monitor well locations within the Wilber Creek and Union Flat Creek Valleys.

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Albion Colfax Pullman

Figure 6-5 Stream gain–loss characteristics (Sinclair and Kardouni, 2009).

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Figure 6-6 Field measurement sites in the Pullman area for the WDOE stream gain-loss study (Sinclair and Kardouni, 2009).

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Figure 6-7 Map showing depth to the top of the Grande Ronde Formation and the proposed surface-water / ground-water study area (After Robischon, 2010a).

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Wanapum Aquifer Study Area

Figure 6-8 Working boundary for the Palouse Ground Water Basin showing study site for the upper aquifer study (after PBAC, 2009c).

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Metamorphic Northern Subarea Kamiak Butte – Angel or intrusive Butte Study Area igneous rocks

Basalt and Western Subarea associated sediments

Pullman – Moscow

Figure 6-9 Generalized geologic map of the Palouse Basin showing the Kamiak Butte – Angel Butte gap study area (Bush and Garwood, 2005d).

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Section 7.0 Task 5 – Conclusions and Recommendations

7.1 Conclusions

7.1.1 General Conclusions The general conclusions of this project are presented below:  The Palouse Ground Water Basin, as currently identified, has poorly defined aquifer boundaries. This stems in part from the location of the Palouse Basin on the eastern margin of the Columbia Plateau. Basalt aquifers and associated ground-water flow systems likely continue into the surrounding area where the Basin boundaries are not defined by contacts with older intrusive igneous or metamorphic rocks. The lack of knowledge relative to aquifer boundaries creates significant problems with respect to defining water budgets and representing basin ground-water systems in numerical models.  Islands of bedrock allow delineation of three subareas within the Palouse Basin. These subareas have been defined as the Pullman–Moscow subarea, the northern subarea and the western subarea. The subarea boundaries are formed by extrapolating through the gaps between bedrock highs. The hydrogeologic conditions within these bedrock gap areas are poorly understood.  Revised names are used for the two major aquifers that occur in the Palouse Basin. The upper aquifer is associated mostly with basalt and sediment of the Wanapum Formation as well as sediment from the underlying Latah Formation (Vantage Member). The surface sediments consisting of loess and alluvium are not considered to be part of the upper aquifer. The lower aquifer is associated mostly with basalt and sediment of the Grande Ronde Formation. The hydraulic gradient is downward between the two aquifers at all locations within the Basin where depth-discrete water-level data are available. The lower aquifer is currently the primary water supply source for the municipalities and the two universities. The upper aquifer is currently a partial water supply source for the City of Moscow and the primary source of water for domestic wells throughout the basin.  Almost all of the hydrogeologic information and most of the ground-water development issues are in the Pullman–Moscow subarea. Thus, the primary focus of the Framework Project has been on the Pullman–Moscow subarea.  Long-term water-level decline has been documented in the lower aquifer within the Pullman–Moscow subarea. Rates of water-level decline have decreased in recent years as a result of a stabilization of pumpage by the four major users (Pullman, Moscow, Washington State University and University of Idaho). Long- term water-level decline also occurred in the upper aquifer in the Moscow area prior to the 1960s when new wells were constructed into the lower aquifer for Moscow and the University of Idaho. Water levels in the upper aquifer in the Moscow area recovered significantly until pumping from the upper aquifer was resumed by the City of Moscow. Water-level decline in the lower aquifer has

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been documented in the City of Palouse wells in the northern subarea. Wells with water-level decline have not been identified in the western subarea  Accurate water balances have not been developed for either the upper or lower aquifers within any of the three subareas within the Palouse Basin. Most of the information in the literature is for the loess-alluvium water balance. Knowledge of surface-water / ground-water interconnection has increased in recent years but still is limited. A hydraulic connection between Paradise Creek and the upper portion of the upper aquifer has been documented based on water-level data on the west side of the University of Idaho campus; however, there is inconclusive evidence as to recharge from the creek to the lower part of the upper aquifer. No data have been identified which show a hydraulic connection between surface water and the lower aquifer within the Palouse Basin.  The uncertainties described above relative to aquifer boundaries and water balance have been major constraints for the construction and calibration of numerical ground-water models. Neither of the models (Barker, 1979; Lum et al., 1990) has accurately predicted impacts from development of the lower aquifer.

7.1.2 Specific Conclusions Specific conclusions for the Framework Project are related to the data gap analysis and include the following:  The western boundary of the lower aquifer within the Pullman–Moscow subarea is not well defined. There is likely a low-hydraulic conductivity zone to the west of Pullman similar to the “barrier zone” described by Barker (1979) and represented in the Barker (1979) and Lum et al. (1990) numerical models. Investigation of the “barrier zone” is an identified high-priority data gap. Construction of production wells west of the “barrier zone” may be a viable water supply alternative for Pullman and Washington State University. Information is needed to investigate the potential hydraulic connection of the lower aquifer with the South Fork of the Palouse River in the reach starting near downtown Pullman and extending about a mile to the northwest. Information from a Washington Department of Ecology study (Sinclair and Kardouni, 2009) suggests significant stream loss occurs in this reach during low stream-flow conditions. This is also an area where the top of the lower aquifer is believed to be close to land surface. Investigation of this area is identified as a high-priority data gap.  Increased water withdrawal from the upper aquifer in the Moscow area is a means to decrease pumping from the lower aquifer and thus decrease the rate of water- level decline in the lower aquifer in the Pullman–Moscow subarea. Analysis of this topic is an identified high-priority data gap.  A monitoring well network that extends throughout the Palouse Basin needs to be established. The purpose of the well network is to collect, perhaps every 10 years, mass water-level measurements in both the upper and lower aquifers. Identified monitoring wells are particularly lacking in the northern and western subareas. The monitoring well network would consist mostly of existing private

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wells but might also include monitoring wells constructed for this purpose in some locations. This investigation is identified as a medium-priority data gap.  The characteristics of the lower aquifer in the bedrock gap separating the Pullman–Moscow subarea from the northern subarea also are poorly understood. Investigation of this area is listed as a medium-priority data gap.  Ongoing research on the delineation of hydraulic sub-basins within the lower aquifer in the Pullman–Moscow subarea is important, particularly if aquifer storage and recovery projects are contemplated in the future. Continuation of this research effort is identified as a medium-priority data gap.  Analysis of the relationship between pumpage rates and rate of water-level decline over the history of the Basin may provide important hydraulic information on the two aquifers in the Pullman–Moscow subarea. The desired product is a temporal plot of total gallons pumped per foot of water level decline for each aquifer for the maximum possible time period. This study is identified as a medium-priority data gap.  Establishment of a well-log database would provide future researchers with readily accessible well-construction data. Development of the database is identified as a medium-priority data gap.  Gaining a greater understanding of the hydrogeology of the surrounding areas is important. This low-priority identified data gap includes investigations of ground-water conditions in surrounding communities such as Colton, Uniontown, Genesee, Palouse, Garfield, and Colfax.

7.2 Recommendations

Recommendations for the Framework Project are described below:  The database created as part of the Palouse Ground Water Basin Framework Project should be maintained and updated as an ongoing effort.  Investigational programs should be initiated to address the identified data gaps. The construction of new monitoring wells will be required as part of several of these efforts. The high-priority data gaps should be addressed first, followed by investigation of selected medium-priority data gaps. The establishment of a monitoring well network should be one of the medium-priority data gaps addressed first.  The list of data gaps provided in this Framework Project report should be evaluated to identify potential university student projects. These could range from master’s thesis projects to senior-design classroom projects. The close working relationship that currently exists between the Palouse Basin Aquifer Committee and researchers at the University of Idaho and Washington State University should be continued into the future.

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Section 8.0 List of References

The List of References is exported from the database and contains additional references which are starred.

2010 Production Well Summary Table for Washington State University Wells Washington State University

2008 Borehole Video Bond Well Palouse Basin Aquifer Committee

2008 Borehole video of Moscow Well No 2. Palouse Basin Aquifer Committee

2008 Borehole video of Moscow Well No. 5 Palouse Basin Aquifer Committee

2006 Post Rehab of University of Idaho Well No. 2 Palouse Basin Aquifer Committee

2004 Borehole video of Moscow New Cemetery Well Palouse Basin Aquifer Committee.

2004 Borehole video of Moscow Old Cemetery well Palouse Basin Aquifer Committee.

2004 Borehole Video of University of Idaho Well No. 2 Palouse Basin Aquifer Committee

2004 Ralph Naylor Farms, LLC: Application for Water Well Permit Number 87-10022 Palouse Basin Aquifer Committee

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2003 Borehole Video of Washington State University (WSU) Well No. 8 Palouse Basin Aquifer Committee.

2002 Borehole Video of the Colfax Fairview Well and Clay Street Well Palouse Basin Aquifer Committee.

2001 Borehole video of Moscow Well No 6. Palouse Basin Aquifer Committee.

2001 Borehole Video of Palouse Well No. 1 Palouse Basin Aquifer Committee.

2000 Borehole video of Moscow Well No 3. Palouse Basin Aquifer Committee

1998 Borehole video of Moscow Elks Golf Course Well Palouse Basin Aquifer Committee.

1978 Washington: A Summary of the Activities of the United States Department of the Interior Geological Survey-Water Resources Division US Geological Survey

1976 Simulation of Hydrology of Primary Basalt Aquifer of the Pullman, Washington-Moscow, Idaho, Basin in Geologic and Hydrologic Principles, Processes, and Techniques

1970 Correspondence Binder 1966 - 1970 PBAC

1961 Ground-Water Investigations in Idaho Geological Survey Research 1961 - Synopsis of Results Agnew, A.F.

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1972 Interstate Ground-Water Aquifers of Washington, Physical and Legal Problems- A Preliminary Assessment State of Washington Water Research Center Report No. 8. Water, Air, and Soil Pollution Vol. 1 Agnew, A.F., and R.W. Busch 1971 Interstate Ground-Water Aquifers of the State of Washington, Physical and Legal Problems – A Preliminary Assessment State of Washington Water Resource Center, Report No. 8; completion report for OWRR, Project A-038-WASH, Agreement No. 14-31-0001-3048

Alley, W.A., R.W. Healy, H.W. LaBaugh, and T.E. Reilly 2002 Flow and Storage in Groundwater Systems Science Compass Review in Science, Vol. 296, pp. 1985 - 1990 Anderson, B.J. 2008 Residential Landscape Water Use and Conservation University of Idaho

Anderson, J.L., M.H. Beeson, R.D. Bentley, K.R. Fecht, P.R. Hooper, A.R. Niem, S.P. Reidel, D.A. Swanson, T.L. Tolan, and T.L. Wright 1987 Distribution Maps of Stratigraphic Units of the Columbia River Basalt Group Washington Division of Geology and Earth Resources Bulletin 77 Anderson, K.E. 1973 Evaluation of Ground Water in the Moscow Pullman Basin Anderson and Kelly Consultants Anderson, R., B. Stasney, and D. Holom 2008 Draft Report, Pullman Well No. 8, Drilling and Testing Results, City of Pullman, Washington Golder Associates Inc. Anderson, R.H., B. Stasney, and A. Douglas 2006 Final Report: Palouse Watershed (WRIA 34) Multi-Purpose Storage Assessment Golder Associates Inc. Badon, N. 2005 Introduction to the Shallow Aquifer Monitoring Project. Palouse Basin Aquifer Committee Badon, N.M. 2007 Implementation of a Groundwater Monitoring Program and Aquifer Testing in the Wanapum Aquifer System, Latah County Idaho

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University of Idaho Badon, N.M. 2007 Thesis Defense: Implementation of a Groundwater Monitoring Program and Aquifer Testing in the Wanapum Aquifer System, Latah County, Idaho University of Idaho Thesis Defense Baines, C.A. 1992 Determination of Sustained Yield for the Shallow Basalt Aquifer in the Moscow Area, Idaho Idaho Water Resources Research Institute Barker, R.A. 1979 Computer Simulation and Hydrogeology of a Basalt Aquifer System in the Pullman-Moscow Basin, Washington and Idaho Washington Department of Ecology, Water Supply Bulletin No. 48 Barker, R.A. 1976 Computer Simulation of a Basalt Aquifer System in the Pullman-Moscow Basin, Washington and Idaho Geological Society of America Cordilleran Section Meeting Abstracts with Programs, Vol. 8, No. 3 Bauer, H.H., and A.J. Hansen Jr. 2000 Hydrology of the Columbia Plateau Regional Aquifer System, Washington, Oregon, and Idaho US Geological Survey Water-Resources Investigations Report 96-4106 Bauer, H.H., and J.J. Vaccaro 1990 Estimates of Ground Water Recharge to the Columbia Plateau Regional, Aquifer System, Washington, Oregon, and Idaho, For Predevelopment and Current Land-Use Conditions US Geological Survey Water Resources Investigation Report 88-4108 Bauer, H.H., and J.J. Vaccaro 1987 Documentation of a Deep Percolation Model for Estimating Ground Water Recharge US Geological Survey Open-File Report 86-596 Bauer, H.H., J. L. Vaccaro, and R.C. Lane 1985 Ground-Water Levels in the Columbia River Basalt Group and Overlying Materials, Spring 1983, Southeastern Washington State US Geological Survey Water-Resources Investigations Report 84-4360 Belknap, B. 1999 Summary of Research Completed on Moscow-Pullman Basin Hydrology Palouse Basin Aquifer Committee

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Bennett, B. 2009 Recharge Implications of Strategic Pumping of the Wanapum Aquifer System in the Moscow Sub-basin University of Idaho Bennett, B. 2009 Recharge Implications of Strategic Pumping of the Wanapum Aquifer System in the Moscow Sub-basin: Thesis Defense University of Idaho Bennett, B. 2009 Thesis Defense: Recharge Implications of Strategic Pumping of the Wanapum Aquifer System in the Moscow Sub-basin University of Idaho Thesis Defense Bennett, B., and J. Osiensky 2009 Strategically Designed Pumping to Maximize Induced Ground Water Recharge to the Wanapum Aquifer System in the Moscow, Idaho Area University of Idaho Poster Bilodeau, K.A. 2009 Pooling our Water Resource Knowledge: Public Knowledge, Concerns, Opinions, and Dynamics Related to Palouse Basin Water Resources Issues University of Idaho Bingham, J.W., and K.L. Walters 1965 Stratigraphy of the Upper Part of the Yakima Basalt in Whitman and Eastern Franklin Counties, Washington. US Geological Survey Professional Paper, 523-C Bloomsburg, G.L. 1969 Comments on Jones & Ross Report “How Long Will the Water Last?” Hand written memo to Cal Warnick Bloomsburg, G.L. 1959 A Water Balance Study of Two Small Watersheds University of Idaho Bockius, S.H., and K.F. Sprenke 1985 Geophysical Mapping of Groundwater Sites in the Moscow Basin Geological Society of America Rocky Mountain Section Program Abstracts Bockius, S.M.

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1985 Geophysical Mapping of the Extent of Basaltic Rocks in the Moscow Groundwater Basin, Latah County, Idaho University of Idaho Bond, J.G., S. A. Price, and P.J. Breeser 1972 Deformational History of the Columbia River Basalts of Western Idaho as Interpreted From Drainage Development Analysis Palouse Basin Aquifer Committee Boucher, P.R. 1970 Sediment Transport by Streams in Palouse river Basin, Washington and Idaho, July 1961- June 1965 US Geological Survey Water Supply Paper 1899-C Brackney, K.M., J. Lee, and T. Bourque 1995 Stormwater Pollution Prevention Plan, Petroleum Contaminated Soil Landfarm Palouse Basin Aquifer Committee Brooks, E., J. Boll, P.A. McDaniel 2004 A Hillslope-Scale Experiment to Measure Lateral Saturated Hydraulic Conductivity Water Resources Research, Vol 40, W04208, doi:10.1029/2003WR002858, 2004 Brooks, E.S, J.F. Kaufman, K.M. Ostrowski, P.A. McDaiel, and J. Boll 2006 Soil Heterogeneity and the Hydrology of the High Precipitation Zone of the Palouse Region ASABE Meeting Presentation, Paper No. 062288 Brooks, E.S., J. Boll, and P.A. McDaniel 2007 Distributed and Integrated Response of a Geographic Information System Based Hydrologic Model in the Eastern Palouse Region, Idaho Hydrological Processes, Vol. 21, pp. 110-122 Brooks, E.S., P.A. McDaniel, and J. Boll 2000 Hydrologic Modeling in Watersheds of the Eastern Palouse: Estimation of Subsurface Flow Contribution Presented at the 2000 PNW-ASAE Regional Meeting, September 21-23, Paper 2000-10 Brown, J.C. 1983 Regional Management Considerations of the Ground Water Resources in Layered Volcanics of Idaho, Oregon, and Washington Washington State Department of Ecology, 83-6 Brown, J.C. 1980

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Stratigraphy and Ground-Water Hydrology of Selected Areas, Columbia Plateau, Washington College of Engineering Research Division, Washington State University Brown, J.C. 1979 Investigation of Stratigraphy and Ground Water Hydrology, Columbia River Basalt Group, Washington College of Engineering Research Report 79/15-37, Washington State University Brown, J.C. 1976 Tectonic Significance of Subsurface Chemical-Stratigraphic Correlation, Pullman-Moscow Basin, Washington and Idaho Geological Society of America, Cordilleran Section, Pullman, Washington Brown, J.C. 1976 Well Construction and Stratigraphic Information: Pullman Test and Observation Well, Pullman, Washington Washington State University College of Engineering research report 76-15-6 Brown, P.A. 2008 Palouse Aquifer Enhanced Recharge Feasibility Project: Draft Report Presentation Golder Associates and HDR Engineering Brown, W.G. 1991 Sensitivity Analysis of a Numerical Model of Ground-Water Flow in the Pullman-Moscow Area, Washington and Idaho Idaho Water Resources Research Institute

Brown, J.C., and T.L. Weber 1976 Report of Borehole Geophysical Investigations University of Idaho Well #4 College of Engineering Research Division, Washington State University Bureau of Land Management 1983 Topographic Map Pullman Washington, Idaho 1:100,000 scale metric, 30x60 Minute Quadrangle Bureau of Land Management Bureau of Reclamation 1972 Lower Snake River Basin, Idaho-Washington Bureau of Reclamation Bush, J. 2008 Geologic Report on Pullman Well No. 8 Golder Associates Inc.

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Bush, J. 2007 Stratigraphic Units of the Palouse Basin Palouse Basin Aquifer Committee Bush, J. 2006a Geologic Report on Moscow Monitoring Wells Palouse Basin Aquifer Committee Bush, J. 2005a Comments on Constructing Lithologic Logs for CRBG Wells Palouse Basin Aquifer Committee. Bush, J. 2005b Figures for: The Columbia River Basalt Group of the Palouse Basin with Hydrological Interpretations, Western Latah County, Idaho, and Eastern Whitman County, Washington Idaho Geological Survey Bush, J. 2005c Moscow Pullman Regional Cross Section Palouse Basin Aquifer Committee Bush, J. 2005d The Columbia River Basalt Group of the Palouse Basin with Hydrological Interpretations, Western Latah County, Idaho, and Eastern Whitman County, Washington DRAFT Idaho Geological Survey Bush, J. 1996 The Geologic History of Moscow and a Model for Moscow’s Ground Water Recharge Palouse Basin Aquifer Committee Bush, J., S. Gill, C. Petrich, and J. Pierce 1999 Geological and Hydrological References: Palouse Region Palouse Basin Aquifer Committee Bush, J.H. 2006b Three Day Short Course on the Palouse Basin Geology and Hydrology Palouse Basin Aquifer Committee Bush, J.H., and D. R. Ralston 1997 Geological Setting of the Eastern Margin of the Columbia Plateau Aquifer System. Inland Northwest Water Resources Conference Bush, J.H.

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1991 Cambrian Paleogeographic Framework of Northeastern Washington, Northern Idaho, and Western Montana Paleozoic Paleogeography of the Western United States - II Bush, J.H., A.P. Provant, and S.W. Gill 1998 Bedrock Geologic Map of the Moscow West Quadrangle Latah County, Idaho, and Whitman County, Washington Idaho Geological Survey, Geologic Map 23 Bush, J.H., and A.P. Provant 1998 Bedrock Geologic Map of the Viola Quadrangle, Latah County, Idaho, and Whitman County, Washington Idaho Geological Survey, Geologic Map 25 Bush, J.H., and D.L. Garwood 2005a (Basin basemap) Palouse Basin Aquifer Committee Bush, J.H., and D.L. Garwood 2005b Bedrock Geologic Map of the Albion 7.5 Minute Quadrangle, Washington Palouse Basin Aquifer Committee Bush, J.H., and D.L. Garwood 2005c Bedrock Geologic Map of the Colfax North 7.5 Minute Quadrangle, Washington Palouse Basin Aquifer Committee Bush, J.H., and D.L. Garwood 2005d Bedrock Geologic Map of the Elberton 7.5 Minute Quadrangle, Washington Palouse Basin Aquifer Committee Bush, J.H., and D.L. Garwood 2005e Bedrock Geologic Map of the Pullman 7.5 Minute Quadrangle, Washington Palouse Basin Aquifer Committee Bush, J.H., and D.L. Garwood 2005f Cross-Sections of the Palouse Basin, Idaho and Washington Palouse Basin Aquifer Committee Bush, J.H., and D.L. Garwood 2005g Fold Map of the Palouse Basin Palouse Basin Aquifer Committee

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Bush, J.H., and D.L. Garwood 2005h Panel Diagram for Wanapum and Grande Ronde Formations, Latah and Whitman Counties Palouse Basin Aquifer Committee Bush, J.H., and D.L. Garwood 2005i Physiographic Map of the Palouse Basin, Washington and Idaho Palouse Basin Aquifer Committee Bush, J.H., and D.L. Garwood 2005j Preliminary Structural Map on the Upper Grande Ronde Surface in the Palouse Basin of Idaho and Washington Palouse Basin Aquifer Committee Bush, J.H., and D.L. Garwood NA Working Draft #1 of Structural Contour Map Including Well Locations Palouse Basin Aquifer Committee Bush, J.H., and D.L. Garwood NA Working Draft #2 of Structural Contour Map Including Well Locations Palouse Basin Aquifer Committee Bush, J.H., and W. Patrick Seward 1992 Geologic Field Guide to the Columbia River Basalt, Northern Idaho Idaho Geological Survey Information Circular 49 Bush, J.H., C.H. Duncan, and D.L. Garwood 2005 Bedrock Geologic Map of the Palouse 7.5 Minute Quadrangle, Washington Palouse Basin Aquifer Committee Bush, J.H., D.L. Garwood, and E.W. Teasdale 2001b Re-Interpretation of the Moscow-Pullman Geology, Idaho-Washington: An Example of the Importance of Geologic Mapping to Ground Water Modeling Palouse Basin Aquifer Committee Bush, J.H., D.L. Garwood, W.L. Oakley III, and T. E. Erdman 2001a Geological Report: Pullman City Well No. 7 Latah Institute of Geological Studies Bush, J.H., D.W. Garwood, and J.J. Hinds 2007a Compiled Bedrock Geologic Map of the Palouse Basin Palouse Basin Aquifer Committee Bush, J.H., J.L. Pierce, and G.N. Potter

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2000 Bedrock Geologic Map of the Moscow East 7.5 Minute Quadrangle, Washington Idaho Geological Survey, Geologic Map 27 Bush, J.H., J.L. Pierce, and G.N. Potter 1998 Bedrock Geologic Map of the Robinson Lake Quadrangle, Latah County, Idaho Idaho Geological Survey, Geologic Map 24 Bush, J.H., K.L. Othberg, and K.L. Priebe 1995 Onaway Member Intracanyon Columbia River Basalt (CRB) Flows, Latah County, Idaho University of Idaho Library Bush, J.H., R.S. Lewis, and K.L. Priebe 2007b Geologic Map of Troy Quadrangle, Latah County, Idaho Idaho Geological Survey, Geologic Map 46 *Caldwell, R.R., and C.L. Bowers 2003 Surface-Water / Ground-water Interaction of the Spokane River and the Spokane Valley / Rathdrum Prairie Aquifer, Idaho and Washington. US Geological Survey Water-Resources Investigations Report 03-4239 Carey, L., and J. Osiensky 2009 Using Tritium Concentrations To Age Date Groundwater in the Palouse Basin Poster for the Palouse Groundwater Summit Cavin, R.C., and J.W Crosby III 1966 Supplemental Geophysical Studies for the City of Moscow, Idaho WSU College of Engineering Research Report 66/9-19 Cavin, R.E. 1964 Significance of the Inter Basalt Sediments in the Moscow Basin, Idaho Washington State University Cherry, J.G. 1986 A Water Balance and Hydrologic Analysis on Crumarine Creek University of Idaho Conrey, R.M., and J.A. Wolff 2010 Basalt Lava Stratigraphy Beneath Pullman and Moscow: Implications for Flow of Groundwater Washington State University

*Corcoran, R. 2010 Personal communication

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Correll, J.S. 1987 Pullman Water System Comprehensive Plan Update CH2M HILL Correll, J.S. 1986 Water Systems Analysis CH2M HILL Cotton Jr., W.R. 1982 Hydrochemistry of Ground Water Near Pullman, Washington Washington State University Crosby III, J. W., and R.L. Fenton 1967 Borehole Geophysical Examination of Moscow City Well No. 6 College of Engineering Research Division, Washington State University Crosby III, J. W., and R.L. Fenton 1967 Borehole Geophysical Examination of Well 14/45-5D3 College of Engineering Research Division, Washington State University Crosby III, J.W. 1968 Ground-Water Hydrology of the Pullman-Moscow Basin, Washington Water resources management and public policy: University of Washington press, p. 93-109 Crosby III, J.W. 1966 Ground-Water Research in the Pullman-Moscow Basin Engineering Geology and Soils Engineering Symposium, 4th Annual, Proceedings: Idaho Department of Highways, p.215-236.

Crosby III, J.W. 1965 Ground-Water Exploration and Development Washington State Institute of Technology Circular 20 Crosby III, J.W. 1965 Ground-Water Exploration and Development Washington State Institute of Technology, Circular 20 Crosby III, J.W. 1964 A Comprehensive Approach to a Local Groundwater Problem New Mexico State University NSF Water Resources Conference

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Crosby III, J.W., and R.M. Chatters 1965 Water Dating Techniques As Applied to the Pullman-Moscow Ground-Water Basin Washington State University, College of Engineering Research Division, Bulletin 296 Crosby III, J.W., and R.E. Cavin 1960 Geologic Investigation of the Moscow Ground Water Basin Employing Geophysical Studies Washington State Institute of Technology Bulletin 250, Washington State University Crosby, J.W., and J.V. Anderson 1971 Some Applications of Geophysical Well Logging to Basalt Hydrogeology Likely published in “Ground Water” Crosthwaite, E.G. 1975 Basic Ground-Water Data for the Moscow Basin, Idaho US Geological Survey Open-File Report Crosthwaite, E.G. 1974 A Progress Report on Results of Test-Drilling and Ground-Water Investigations of the Snake Plain Aquifer, Southeastern Idaho, Part 3 - Lake Walcott-Bonanza Lake Area Idaho Department of Water Resources, Water Information Bulletin No. 38 DeMotte, H., and W.F. Miles 1933 A Study of the Pullman Artesian Basin State College of Washington Doke, J.L., and G.S. Hashmi 1994 Paradise Creek Watershed Characterization Study State of Washington Water Research Center prepared for the Palouse Conservation district Douglas, A. A. 2004 Radiocarbon Dating as a Tool for Hydrogeological Investigations in the Palouse Basin University of Idaho Douglas, A. A., J.L. Osiensky, and C.K. Keller 2007 Carbon-14 Dating of Ground Water in the Palouse Basin of the Columbia River Basalts Journal of Hydrology, Vol. 334, pp. 502-512 Douglas, S. 2006 Grande Ronde Aquifer Test April 11, 2006 Preliminary Results Palouse Basin Aquifer Committee Drost, B.W., K.J. Whiteman, and J.B. Gonthier

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1990 Geologic Framework of the Columbia Plateau Aquifer System, Washington, Oregon and Idaho US Geological Survey Water Resources Investigation Report 87-4238 Eakin, T.E. 1946 (Water levels and artesian pressure in US in 1943) US Geological Survey Water Supply Paper 990, pp. 8-10 EBASCO Services 1958 Supplemental Water Supply for Moscow, Idaho: Interim Report Phase 1 Preliminary Reconnaissance and Consultation EBASCO Fairley, J. P., M.D. Solomon, J.J. Hinds, G.W. Grader, J.H. Bush, and A. L. Rand 2006 Latah County Hydrologic Characterization Report Idaho Department of Water Resources Fealko, J.F. 2003 A Probabilistic Water Resources Assessment of the Paradise Creek Watershed University of Idaho Fiedler, A. 2009 Thesis Defense: Well Interference Effects in the Grande Ronde Aquifer System in the Moscow- Pullman Area of Washington and Idaho University of Idaho Thesis Defense Fiedler, A. 2009 Well Interference Effects in the Grande Ronde Aquifer System in the Moscow-Pullman Area of Washington and Idaho University of Idaho Filler, J.R., and C.C. Warnick 1982 Hydrologic Flow Determination for Hydropower Feasibility Analysis Research Technical Completion Report, Project A-068-IDA, Idaho Water and Energy Resources Research Institute

Fjelstad, A., N. Bladow, S. Neeley, and T. Romanick. 2008 Palouse Ridge Golf Course Alternative Water Source Feasibility Study Washington State University Foxworthy, B.L., and R.L. Washburn 1963 Ground Water in the Pullman Area, Whitman County, Washington US Geological Survey Water Supply Paper 1655

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Gay, A.E. 2009 Sky View Estates Long-Term Water Supply Report USKH Consulting report prepared for Developers of the Palouse Geyer, D.J., C.K. Keller, J.L. Smith, and D.L. Johnstone 1992 Subsurface Fate of Nitrate as a Function of Depth and Landscape Position in Missouri Flat Creek Watershed, U.S.A. Journal of Contaminant Hydrology Gill, S. 1998 Elk’s Golf Course Aquifer Test Analysis Elk’s Golf Course Golder Associates, Inc. 2007 WRIA 34 Water Quality Supplemental Assessment. Golder Associates, Inc. Golder Associates, Inc. 2005 Phase II – Level 1 Technical Assessment for the Palouse Basin (WRIA 34) Golder Associates Inc. Golder Associates, Inc. 2001 Pullman Well No. 7, Drilling and Testing Results, City of Pullman, Washington. Golder Associates Inc. Golder Associates, Inc. and Dally Environmental 2009 Palouse Watershed Detailed Implementation Plan Golder Associates Inc Golder Associates, Inc. and HDR Engineering 2008 Palouse Aquifer Enhanced Groundwater Recharge Feasibility Project Report Consulting report prepared for the Palouse Conservation District Graham, W.G., and L.J. Campbell 1981 Ground Water Resources of Idaho Idaho Department of Water Resources

*Gregory, Guy 2010 Personal Communication Gulick, C.W. 1994

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Geologic Map of the Pullman 1:100,000 Quadrangle, Washington-Idaho Washington Division of Geology and Earth Resources, Open File Report 94-6 Hansen, Jr., A.J., J.J. Vaccaro, and H.H. Bauer 1994 Ground Water Flow Simulation of the Columbia Plateau Regional Aquifer System, Washington, Oregon and Idaho. US Geological Survey Water Resources Investigation Report 91-4187 Hart Crowser 1990 Draft: Monitoring Well Installation Sampling and Analysis Report Whitman County Landfill, Whitman County Washington Hart Crowser Hart Crowser 1989 Monitoring Well Installation and Sampling Report Groundwater Monitoring Program Whitman County Landfill Hart Crowser Hathhorn, W.E., and M.E. Barber 1994 Hydrogeologic Boundary Assessment for the Pullman-Moscow Basin Clearwater Consultants Project Completion Report Haynes, B., and H. Harrington 2004 Background on Petition for IDWR Action on Palouse Aquifers Presentation given to the Idaho Legislature’s Expanded Natural Resource Interim Committee: North Idaho Working Group

HDR 2008 City of Pullman Water System Plan Update HDR HDR EES and Golder Associates, Inc. 2007 Palouse Watershed Plan Golder Associates Inc. Heath, R.C. 1983 Basic Ground-Water Hydrology US Geological Survey, Water-Supply Paper 2220 Heinemann, R. 1994 The Relation Between Streams and Ground-Water Flow Systems Within the Pullman-Moscow Area of Washington and Idaho University of Idaho

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Hernandez, H. 2006 Hydrogeologic Characterization of Interaction Between Paradise Creek and Wanapum Aquifer UPDATE Palouse Basin Aquifer Committee Hernandez, H.P. 2007 Observations of Recharge to the Wanapum Aquifer System in the Moscow Area, Latah County, Idaho University of Idaho Holm, D. 2006 The Pre-Basalt Basement Geometry Delineated by Gravity Measurements Near Kamiak Butte, Eastern Washington Palouse Basin Aquifer Committee. Holom, D. 2006 Ground Water Flow Conditions Related to the Pre-Basalt Basement Geometry Delineated by Gravity Measurements Near Kamiak Butte, Eastern Washington University of Idaho Holom, D. 2004 A Study of Rock Lake Washington as the Potential Discharge Zone of the Grande Ronde Aquifer Using Oxygen Isotope Analysis Report prepared for Jim Osiensky, Professor of Hydrology, University of Idaho Hooper, P.R. 1982 The Columbia River Basalts Science, Vol. 215, No. 4539; pp. 1463 - 1468 Hooper, P.R., and G.D. Webster 1982 Geology of the Pullman, Moscow West, Colton, and Uniontown, 7 ½ Minute Quadrangles, Washington and Idaho Washington State Department of Natural Resources, Division of Geology and Earth Resources Hopster, D. 2003 A Recession Analysis of Springs and Streams in the Moscow-Pullman Basin University of Idaho Howard Consultants, Inc. (including Dale Ralston) 1995 Hydrogeologic Evaluation and Development of a Monitor Well Network, Whitman County Landfill, Washington Consulting report prepared for Whitman County

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Hubbard, C.R. 1956 Clay Deposits of North Idaho Idaho Bureau of Mines and Geology, Pamphlet No. 109 Hudak, J.J. 1993 Pullman Water Plan City of Pullman Hutchins, W.A. 1956 Idaho Law of Water Rights Idaho State Department of Reclamation Idaho Department of Environmental Quality 2001 City of Moscow, Source Water Assessment Final Report Idaho Department of Environmental Quality Idaho Legislature 2004 Legislative Council Interim Committee Natural Resource Issues 2003 - 2004 Legislative Council Interim Committee Natural Resource Idaho Legislature 2004 Senate Concurrent Resolution 103 Web; R:\Reports\Electronic files from PBAC\References\2004_Interim_Committee_SENATE CONCURRENT RESOLUTION NO_ 103 - Natural resource issues, study.htm

Idaho Legislature: Expanded Natural Resource Interim Committee, North Idaho Working Group 2004 North Idaho Working Group Meeting Minutes Legislative Council Interim Committee Natural Resource Jackson, D.B. 1976 D.C. Resistivity Studies Near Moscow, Idaho and Pullman, Washington Geological Society of America, Cordilleran section, Pullman, Washington Jackson, D.B. 1975 Schlumberger Soundings in the Moscow, Idaho and Pullman, Washington Area US Geological Survey Open file report 75-584 Jacobson, J. 2007 Stretch Potential with Data Loggers Reel Material University of Idaho Jacobson, J., and J.L. Osiensky

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2007 Stretch Potential with Data Loggers Reel Material University of Idaho Jeffrey C. Brown and T.L. Weber 1976 Report of Borehole Geophysical Investigations University of Idaho Well #4 College of Engineering Research Division, Washington State University Johnson, G.S., G. Bloomsburg, and D.R. Ralston 1996 Evaluation and Modification of the Pullman-Moscow Ground-Water Flow Model Idaho Water Resources Research Institute, University of Idaho Johnson, L.C., and M. Molnau 1975 Hydrograph and Water Quality Relationships for Two Palouse Cropland Watersheds University of Idaho, College of Agriculture, Research Bulletin No. 87 Johnson, M.M., and C.F. Myrene 1929 The Geology and Economic Resources in a Portion of Latah County, Idaho in the Vicinity of Moscow, Idaho University of Idaho Johnson, W.F. 1973 Comprehensive Water Plan for Washington State University 1973 Washington State University Jones, R.W. 1961 Water and Mineral Resources of the Palouse Northwest Science Jones, R.W., and S.H. Ross 1969 Detailed Ground Water Investigation of Moscow Basin Research Technical Completion Report A-011 IDA, Water Resources Research Institute, University Idaho Jones, R.W., and S.H. Ross 1972 Moscow Basin Ground Water Studies Idaho Bureau of Mines and Geology, Pamphlet 153 Jones, R.W., and S.H. Ross 1969 Moscow Basin Ground Water Problem - How Long Will the Water Last? Proceedings of the Engineering Geology and Soils Symposium Jones, R.W., S.H. Ross, and R.E. Williams 1968

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Feasibility of Artificial Recharge of a Small Ground Water Basin by Utilizing Seasonal Runoff from Intermittent Streams Proceedings of the 6th Annual Engineering Geology and Soils Engineering Symposium; University of Idaho, Idaho Water Resources Research Institute

Jones, W.V. 1966 A Study of Ground Water Movement in Landslides NA Kaal, A.S. 1978 Analysis of Hydrogeologic Factors for the Location of Water Wells in the Granitic Environment of Moscow Mountain, Latah County, Idaho University of Idaho Keller, C.K. 2007 Grande Ronde Aquifer Hydrogeology in the Pullman Moscow Region: Some Key Features Affecting Ground Water Exploitability Cornelius et al. vs. Washington Department of Ecology and WSU, PCHB No. 06-099 Keller, C.K., C.N. Butcher, J.L. Smith, and R.M. Allen-King 2008 Nitrate in Tile Drainage of the Semiarid Palouse Basin Journal of Environmental Quality, Vol. 37, pp. 353-361 Klein, D.P., R.A. Sneddon, and J.L. Smoot 1987 Magnetotelluric Study of the Thickness of Volcanic and Sedimentary Rock in the Pullman- Moscow Basin of Eastern Washington US Geological Survey Open File Report 87-140 Kopp, W. P. 1994 Hydrogeology of the Upper Aquifer of the Pullman-Moscow Basin at the University of Idaho Aquaculture Site University of Idaho Landes, H. 1905 Preliminary Report on the Waters of Washington US Geological Survey, Water Supply and Irrigation Paper No. 111, Series 0, Underground Waters, 29 Lane, R.C., and K. J. Whiteman 1989 Ground Water Levels, Spring 1985, and Ground Water Level Changes, Spring 1983 to Spring 1985, in Three Basalt Units Underlying the Columbia Plateau, Washington and Oregon. US Geological Survey Water Resources Investigations Report 88-4018 Laney F.B., V.R.D. Kirkham, and A.M. Piper

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1923 Ground Water Supply at Moscow, Idaho Idaho Bureau of Mines and Geology Pamphlet No. 8; retyped by IGS in 1985 Larson, K.R. 1997 Stable Isotopes in the Pullman Moscow Basin, Eastern Washington and North Idaho: Implications for the Timing, Magnitude and Distribution of Ground Water Recharge Washington State University Larson, K.R. 1997 Thesis defense video: Stable Isotopes in the Pullman Moscow Basin, Eastern Washington and North Idaho: Implications for the Timing, Magnitude and Distribution of Ground Water Recharge Washington State University Larson, K.R., C.K. Keller, P.B. Larson, and R.M. Allen-King 2000 Water Resources Implications of 18O and 2H Distributions in a Basalt Aquifer System Ground Water, Vol. 38, No. 6, pp. 947-943 Larson, K.R., C.K. Keller, R.M. Allen-King, W.E. Hathhorn, and P.B. Larson 1996 Groundwater Recharge and Residence Times in the Pullman-Moscow Basin: A Stable Isotope Study Project Status Report for the State of Washington Water Resource Center and the US Department of the Interior; Water Resource Center Project A-196-WASH, US DOI grant G2053-17 Latah County Board of Commissioners 2005 Board of Commissioners Motion and Order, Latah County Ordinance No. 258, Moscow Sub- basin Groundwater Management Overlay Zone Latah County Latah County Board of Commissioners 2005 Board of Commissioners Motion and Order, Latah County Ordinance No. 260, Moscow Sub- basin Groundwater Management Overlay Zone Latah County Lawrence, W.R. 1995 Hydrogeological Assessment of the Potential for Future Ground-Water Development in Genesee, Idaho University of Idaho Leek, F. 2006 Cross Section Along the Union Flat Creek Palouse Basin Aquifer Committee

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Leek, F. 2006 Farida Leek GIS data 1 Palouse Basin Aquifer Committee Leek, F. 2006 Farida Leek GIS data 2 Palouse Basin Aquifer Committee Leek, F. 2006 Hydrogeologic Characterization of the Palouse Basin Basalt Aquifer System Washington and Idaho Washington State University Leek, F. 2006 Progress Report: Hydrogeological Characterization of the Palouse Basin Basalt Aquifer System Palouse Basin Aquifer Committee Leek, F. 2006 Reference Database Palouse Basin Aquifer Committee Leek, F. 2006 References (From Farida Leek Data) Palouse Basin Aquifer Committee. Li, T. 1991 Hydrogeologic Characterization of a Multiple Aquifer Fractured Basalt System University of Idaho Lin, C.L. 1967 Factors Effecting Ground-Water Recharge in the Moscow Basin, Latah County, Idaho Washington State University Lin, H., E. Brooks, P. McDaniel, and J. Boll 2008 Hydropedology and Surface/Subsurface Runoff Processes Encyclopedia of Hydrological Sciences, John Wiley & Sons, Ltd. Lockwood Jr., P. 1996 Analysis of Downhole Dissolved Oxygen Measurements in Shallow Aquifers near Moscow, Idaho University of Idaho

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Long, P.E. 1987 Review of Evidence for the Quenching Origin of Entablatures in Columbia River Basalt Flows Palouse Basin Aquifer Committee Lum II, W.E., J.L. Smoot, and D.R. Ralston 1990 Geohydrology and Numerical Model Analysis of Ground-Water Flow in the Pullman-Moscow Area, Washington and Idaho US Geological Survey, Water Resources Investigations Report 89-4103 Luzier, J.E., and A. Skrivan 1975 Digital Simulation and Projection of Water Level Declines in Basalt Aquifers of the Odessa Lind Area, East Central Washington US Geological Survey Water Supply Paper 2036 Luzier, J.E., and R.J. Burt 1974 Hydrology of Basalt Aquifers and Depletion of Ground Water in East-Central Washington State of Washington, Department of Ecology, Water Supply Bulletin No. 33 Lyman, R.A. 1991 Residential Water Demand: Some New Results University of Idaho Machlis, G.E. 1986 The Conservation of Water in Moscow, Idaho: A Survey of Public Opinion Idaho Water Resources Research Institute Mangan, M., and T.L. Wright 1984 Regional Correlation of Grande Ronde Basalt Flows, Columbia River Basalt Group. American Geophysical Union Transactions, Vol. 65 Mangan, M.T., T.L. Wright, and D.A. Swanson 1986 Regional Correlation of Grande Ronde Basalt Flows, Columbia River Basalt Group, Washington, Oregon and Idaho. Geological Society of America Bulletin Mann, H., J. Baldwin, and K. Brackney 2005 Isotopic Age Dating of Municipal Water Wells in the Lewiston Basin, Idaho Ground Water Quality Technical Report No. 24 - Idaho Department of Environmental Quality Marose, R. 2003 Water Strike Muddies Aquifer Debate; Sherman: Discovery Shows Need for More Research, Less Panic

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Moscow Pullman Daily News Martin, T.L., and D. DeFrancesco 2007 Final Palouse River Watershed Instream Flow Needs Assessment Golder Associates Inc. McDaniel, P., M.P. Regan, E. Brooks, J. Boll, S. Barndt, A. Falen, S.K. Young, and J.E. Hammel 2008 Linking Fragipans, Perched Water Tables, and Catchment Scale Hydrological Processes Catena, Vol. 73, pp. 166-173 McVay, M. 2007 Grande Ronde Aquifer Characterization in the Palouse Basin University of Idaho McVay, M. 2007 Thesis defense video: Grande Ronde Aquifer Characterization in the Palouse Basin University of Idaho Mellin, J. 2001 Estimate of Seasonal Water Runoff From the Moscow Mountain Front, Moscow, Idaho Palouse Basin Aquifer Committee Moran, H.L. 1970 Methodology for Evaluating Surface Water Reservoir Sites University of Idaho Moran, K. 2009 Long-Term, Basin-Wide Grande Ronde Aquifer Test Poster for the Palouse Groundwater Summit Moravec, B.G., C.K. Keller, J.L. Smith, R.M. Allen King, A.J. Goodwin, J.P. Fairley, and P.B. Larson 2010 Oxygen 18 Dynamics in Precipitation and Streamflow in a Semi Arid Agricultural Watershed, Eastern Washington, USA Hydrological Processes, Vol. 24, pp. 446-460 Morgan, D.S., R.S. Dinicola, and J.R. Bartilino 2008 Ground Water Availability Assessment for the Columbia Plateau Regional Aquifer System, Washington, Oregon and Idaho US Geological Survey Ground-Water Resources Program Murray, J., A.T. O’Geen, and P.A. McDaniel

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2003 Development of a GIS Database for Ground-Water Recharge Assessment of the Palouse Basin Soil Science, Vol. 168, No. 11, pp. 759-768 Nadler, M. 1981 Feasibility Study: Reclaimed Wastewater for Ground Water Recharge at Moscow, Idaho University of Idaho Civil Engineering Department Nassar, E.G., and K.L. Waters 1975 Water in the Palouse River Basin, Washington Washington Department of Ecology Water-Supply Bulletin 39 Newcomb, R.C. 1986 Ground Water in Columbia River Basalt Hydrogeology of Volcanic Terrains Newcomb, R.C. 1962 Storage of Ground Water Behind Sub Surface Dams in The Columbia River Basalt, Washington, Oregon and Idaho US Geological Survey Professional Paper 383-A Nimmer, R.E. 2006 Shallow Aquifer Drought (SAD) Monitoring Program Palouse Basin Aquifer Committee Nimmer, R.E. 2005 Electrical Characterization of a Three-Phase, Tracer, Injection Test University of Idaho Nimmer, R.E. 1998 Ground Water Tracer Studies in Columbia River Basalt University of Idaho Nimmer, R.E., D.R. Ralston, A.H. Wylie, and G.S. Johnson 2001 Recirculating Tracer Test in Fractured Basalt Geological Society of America, Special Paper 353 North Pacific Division Corps of Engineers 1972 Pumped-Storage Potential of Pacific Northwest Prepared for: Power Planning Committee, Pacific Northwest River Basins Commission O’Brien, R., and C.K. Keller 1993

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Estimation of Groundwater Recharge in the Palouse Loess Using Environmental Tritium Project Completion Report for the State of Washington Water Resource Center and the US Department of the Interior; Water Resource Center Project A-172-WASH, US DOI grant G2053-03

O’Brien, R., C.K. Keller, and J.L. Smith 1996 Multiple Tracers in Shallow Ground-Water Flow and Recharge in Hilly Loess Ground Water, Vol. 34, No. 4, pp. 675-682 O’Geen, A.T. 2002 Assessment of Hydrologic Processes Across Multiple Scales in Soils/Paleosol Sequences Using Environmental Tracers University of Idaho O’Geen, A.T., P.A. McDaniel, and J. Boll 2002 Chloride Distributions as Indicators of Vadose Zone Stratigraphy in Palouse Loess Deposits Vadose Zone Journal, Vol. 1, pp. 150 – 157 O’Geen, A.T., P.A. McDaniel, J. Boll, and C.K. Keller. 2005 Paleosols as Deep Regolith: Implications for Ground-Water Recharge Across a Loessial Climosequence. Geoderma, Vol. 126, pp. 85-99 O’Geen, A.T., P.A. McDaniel, J. Boll, and E. Brooks 2003 Hydrologic Processes in Valley Soilscapes of the Eastern Palouse Basin in Northern Idaho Soil Science, Vol. 168, No. 12, pp. 846-855 Opatz, C. 2007 Thesis Defense: Evaluation of Cleaning and Rehabilitation of University of Idaho Well #2 on the Local Groundwater Systems, in the Moscow, Idaho Area University of Idaho Thesis Presentation Opatz, C. 2006 Progress Report: UI Well #2 Passive Drainage Well Project Palouse Basin Aquifer Committee Opatz, C.C. 2007 Evaluation of Cleaning and Rehabilitation of University of Idaho Well #2 on the Local Groundwater Systems, in the Moscow, Idaho Area University of Idaho Osiensky, J. 2006 Continued Monitoring of the Grande Ronde Aquifer System Water Levels with an Emphasis on

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Hydraulic Testing and Maximizing the Benefits from the New Monitoring Well Fields Palouse Basin Aquifer Committee Othberg, K.L., and R. M. Brechenridge 2001 Surficial Geologic Map of the Moscow East Quadrangle and Part of the Moscow West Quadrangle, Latah County Idaho Idaho Geological Survey Owsley, D. 2003 Characterization of Grande Ronde Aquifers in the Palouse Basin Using Large Scale Aquifer Tests University of Idaho Pacific Groundwater Group 2009 Well completion Report for Hawkins Companies Wells, Whitman County, Washington Consulting report prepared for Hawkins Companies Palouse Basin Aquifer Committee 2009a 2006-2009 Municipal Pumping and Water-Level Records Palouse Basin Aquifer Committee. Palouse Basin Aquifer Committee 2009b Palouse Basin Aquifer Committee Monitoring Data Palouse Basin Aquifer Committee

*Palouse Basin Aquifer Committee 2009c 2008 Annual Report – Palouse Ground Water Basin Water Use Report Palouse Basin Aquifer Committee Palouse Basin Aquifer Committee 2004 Presentation to the Idaho Legislature’s Expanded Natural Resource Interim Committee: North Idaho Working Group Presented to or handed out at the Idaho Legislature’s Expanded Natural Resource Interim Committee: North Idaho Working Group

*Palouse Basin Aquifer Committee 2001 2000 Annual Report – Water Use in the Palouse Basin Palouse Basin Aquifer Committee

*Palouse Basin Aquifer Committee 2000 1999 Annual Report Palouse Basin Aquifer Committee

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Palouse Conservation District and Paradise Creek Management Committee 1997 Paradise Creek Watershed Water Quality Management Plan Palouse Conservation District and Paradise Creek Management Committee Pardo, B.G. 1993 Relation of Groundwater and Surface Water at the University of Idaho Groundwater Research Site University of Idaho Pierce, J.L. 1998 Geology and Hydrogeology of the Moscow East and Robinson Lake Quadrangles, Latah County, Idaho University of Idaho Piper, A.M. Ground Water for Municipal Supply at Moscow, Idaho The Idaho Engineer Pitz, C.F. 2006 An Evaluation of a Piezometer-Based Constant Head Injection Test (CHIT) for use in Groundwater / Surface Water Interaction Studies Department of Ecology Report, 06-03-042 Porcello, J.J. 2009 A Conceptual Ground Water System Model for the Columbia River Basalt Group (CRBG) in the Columbia Basin Ground Water Management Area (GWMA) of South Central Washington Geological Society of America Annual Meeting 2009 Priesto, C., C. Perkins, and E. Berkman 1985 Columbia River Basalt Plateau – An Integrated Approach to Understanding Basalt –Covered Areas Geophysics, Vol. 50, No. 12, pp. 2709-2719 Provant, A.P. 1995 Geology and Hydrogeology of the Viola and Moscow West Quadrangles, Latah County, Idaho and Whitman County, Washington University of Idaho Pullman Moscow Water Resources Committee 1992 Ground Water Management Plan Pullman Moscow Water Resources Committee Pullman Moscow Water Resources Committee 1969

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Pullman Moscow Water Resources Committee Status Report Pullman Moscow Water Resources Committee *Ralston, D.R. 2010 Personal communication Ralston, D.R. 2009 Review of Sky View Estates Water Supply Potential Memorandum from Dale Ralston to Latah County Board of Commissioners Ralston, D.R. 2009 Revised Review of Sky View Estates Water Supply Potential Memorandum from Dale Ralston to Latah County Board of Commissioners Ralston, D.R. 2007 Memorandum: Completion of Moscow Test Well Project Memo to Helen Harrington, Idaho Department of Water Resources Ralston, D.R. 2006 Hydrogeologic and Monitoring Well Evaluation of the Whitman County Carothers Road Solid Waste Facility Ralston Hydrologic Services, Inc. Ralston, D.R. 2004 Hydrologic Conditions in the Palouse Aquifer Presentation given to the Idaho Legislature’s Expanded Natural Resource Interim Committee: North Idaho Working Group

Ralston, D.R. 2000 Report of Construction and Testing of a New Well for the City of Palouse, Washington. Ralston Hydrologic Services Ralston, D.R. 1996 Analysis of Ground Water Development Potential for the City of Palouse, Washington Ralston Hydrologic Services Ralston, D.R. 1972 Guide for the Location of Water Wells in Latah County Idaho Bureau of Mines and Geology, Information Circular Number 23 Ralston, D.R., and J.L. Smoot 1989 Ground Water in the Pullman-Moscow Area, A Water Supply for the Future? Idaho Water Resources Research Institute

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Ralston, D.R., D.L. Grant, H. L.Schatz, and D. Goldman 1974 Analysis of the Impact of Legal Constraints on Groundwater Resource Development in Idaho Idaho Bureau of Mines, Pamphlet No. 158 Ralston, D.R., and E.J. Kozak 1970 Ground Water Development in Idaho 1969 Idaho Department of Reclamation Reeves, M. 2009 Estimating Recharge Uncertainty using Bayesian Model Averaging and Expert Elicitation with Social Implications University of Idaho Reidel, S.P. 1983 Stratigraphy and Petrogenesis of Grande Ronde Basalt From the Deep Canyon Country of Washington, Oregon and Idaho. Geological Society of America Bulletin, Vol. 94 Rember, W.C., and E. H. Bennett 1979 Geologic Map of Pullman Quadrangle, Idaho Idaho Geological Survey Richardson, T. 2010 Personal communication Ringe, L.D. 1968 Geomorphology of the Palouse Hills, Southeastern Washington University of Idaho Robinette, M. 1975 Geophysical Investigations of Washington’s Ground Water Resources College of Engineering Research Division, Washington State University Robinette, M.S. 1979 Geophysical Investigations of the Pullman, Washington – Moscow, Idaho Basin Proceedings of the 17th Annual Engineering Geology and Soils Engineering Symposium Robischon, S. 2010a Depth to Grande Ronde map Palouse Basin Aquifer Committee

Robischon, S. 2010b

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Comparison of Upper Aquifer Well Water Levels to Paradise Creek Discharge Presentation given at the Palouse Basin Aquifer Committee meeting in April

*Robischon S. 2010 Personal communication Ross, C.P., and J.D. Forrester 1958 Outline of the Geology of Idaho Idaho Bureau of Mines, Bulletin 15 Ross, S. 1964 Moscow Basin Basic Data (Well Logs), Ross Open File Report Palouse Basin Aquifer Committee Ross, S.H. 1965 Contributions to the Geohydrology of Moscow Basin, Latah County, Idaho Idaho Bureau of Mines and Geology, Open File Report Russell, I.C. 1897 A Reconnaissance in Southeastern Washington Water Supply and Irrigation Papers of the US Geological Survey No. 4 Schuster, J.E., C.W. Gulick, S.P. Reidel, K.R. Fecht, and S. Zurenko 1997 Geologic Map of Washington – Southeast Quadrant Washington Division of Geology and Earth Resources, Geologic Map GM-45 Sherman, C. 2007 Boundary Conditions Between the City of Moscow and the City of Pullman University of Idaho. Sherman, C. 2007 Boundary Conditions Between the City of Moscow and the City of Pullman University of Idaho. Siath, J. 1973 Water Supply Study for the City of Moscow City of Moscow Siems, B.A., J.W. Crosby III, J.V. Anderson, J.H. Bush and T.L. Weber 1973 Final Report 1972/1973: Geophysical Investigations of Washington’s Ground Water Resources College of Engineering Research Division, Washington State University Silar, J.

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1969 Ground Water Structures and Ages in the Eastern Columbia Basin, Washington Washington State University College of Engineering Research Division, Bulletin 315 Sinclair, K.A., and J.D. Kardouni 2009 Surface-Water/Groundwater Interactions and Near-stream Groundwater Quality along the Palouse River, South Fork Palouse River and Paradise Creek Washington Department of Ecology, Publication No. 09-03-007 Sisco, H.G. 1976 Ground Water Levels and Well Records for Discontinued Observation Wells in Idaho 1915-72; Part A US Geological Survey, Basic-Data Release 3 Smoot, J. L. 1987 Hydrogeology and a Mathematical Model of Ground-Water Flow in the Pullman-Moscow Region, Washington and Idaho University of Idaho Smoot, J., and D.R. Ralston 1984 Inputs and Outputs to Streams in the Moscow Pullman Basin, Idaho and Washington University of Idaho Smoot, J.L., and D.R. Ralston 1987 Hydrogeology and a Mathematical Model of Ground-Water Flow in the Pullman-Moscow Region, Washington and Idaho Idaho Water Resources Research Institute Snyder, D.T., and J.V. Haynes 2010 Groundwater Conditions During 2009 and Changes in Groundwater Levels from 1984 to 2009, Columbia Plateau Regional Aquifer System, Washington, Oregon, and Idaho US Geological Survey Groundwater Resources Program, Scientific Investigations Report 2010- 5040 Sokol, D. 1966 Interpretation of Short Term Water Level Fluctuations in the Moscow Basin Latah County Idaho Idaho Bureau of Mines and Geology Pamphlet 137 Solomon, M., and K. Brackney 2007 Letter Re. Pacific Groundwater Group 6/4/07 Response Letter NA Stasney, B., T. White, and R. Anderson 2004

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Well No. 3 Replacement- Data Review and Siting Report Golder Associates Inc. Stevens, J.W., and D. R. Haller 2001 Water System Plan Update Volume 1 Gray & Osborne, Inc Stevens, J.W., and D.R. Haller 2001 Water System Plan Update Volume 2 Gray & Osborne, Inc Stevens, P.R. 1960 Ground-Water Problems in the Vicinity of Moscow, Latah County, Idaho US Geological Survey Water Supply Paper 1460-H Stevens, Thompson & Runyan, Inc 1973 The Feasibility of Union Flat Creek Pumped Storage Stevens, Thompson & Runyan, Inc Stevens, Thompson & Runyan, Inc. 1970 Water Supply Study Prepared for the Pullman Moscow Water Resources Committee Swanson, D.A. 1987 Regional Variation in Jointing Style in Grande Ronde Basalt Related to Miocene Geography, Columbia Plateau Geological Society of America Abstracts with Programs, Vol.19, No.6, pp 455-456 Swanson, D.A., J.L. Anderson, R.D. Bently, G.R. Byerly, V.E. Camp, and T.L. Wright 1980 Newly Completed Geologic Map of the Columbia River Basalt Group Geological Society of America(?) Cordilleran Section Abstracts with Programs Teasdale, E.W. 2002 Hydrogeologic Sub-Basins in The Palouse Area of Idaho and Washington University of Idaho Ten Eyck, G., and C. Warnick 1984 Catalog of Water Reports Pertinent to the Municipal Water Supply of Pullman, Washington and Moscow, Idaho – A Summary Idaho Water and Energy Resources Research Institute, University of Idaho The Mountain Resource Group 1993 Eastern Columbia Plateau Aquifer System Sole Source Aquifer Investigation

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Palouse Clearwater Environmental Institute Thomas, Dean & Hoskins, Inc. and Geoengineers, Inc. 1999 Wellhead Protection Program Plan Thomas, Dean & Hoskins, Inc. and Geoengineers, Inc. Trihey, E.W. 1973 Completion Report on the Well Altitude Survey in the Moscow Sub-Basin, Idaho US Geological Survey Tullis, E.L. 1944 Contributions to the Geology of Latah County Bulletin of the Geological Sciences of America, Vol. 55, No. 2 Tungate, A.M. 1995 Hydrographs of Water Levels in Observation Wells in Idaho, 1944-93 US Geologic Survey Open File Report 95-458 US Army Corps of Engineers 1989 Reconnaissance Report Palouse River Basin Idaho and Washington US Army Corps of Engineers US Army Corps of Engineers 1976 Public Meeting Pullman, Washington: Palouse Pumped Storage Study Department of the Army, Walla Walla District, Corps of Engineers US Army Corps of Engineers 1976 Pumped-Storage in the Pacific Northwest, an Inventory US Army Corps of Engineers, North Pacific Division US Army Corps of Engineers 1975 Pumped Storage in the Pacific Northwest, What? When? Where? Ten Frequently Asked Questions US Department of the Army Corps of Engineers, North Pacific Division *United States Geological Survey (USGS) Accessed May 2010 USGS Surface Water Daily Data for the Nation: US Geological Survey 1964 Topographic Map, Pullman Quadrangle, Whitman County, Washington, 7.5 Minute Series US Geological Survey

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Vaccaro, J. 1986 Columbia Plateau Basalt Regional Aquifer-System Study US Geological Survey Circular 1002 Vaccaro, J.J. 1999 Summary of the Columbia Plateau Regional Aquifer-System Analysis, Washington, Oregon, and Idaho US Geological Survey Professional Paper 1413-A Vaccaro, J.J. 1987 Estimation of the Spatial and Temporal Variation of the Temporal Distributions of Evapotranspiration and Deep Percolation, Part II Application to the Columbia Plateau, Washington, Oregon and Idaho EOS, Vol. 68, No. 44 Vaccaro, J.J., and H.H. Bauer 1990 Archiving of Deep Percolation Models, Data Files, and Calculated Recharge Estimates for the Columbia Plateau Regional Aquifer System, Washington, Oregon, and Idaho US Geological Survey Open File Report 88-186 Vivian, R.W. 1979 Water System Study Update STRAAM Engineers, Inc. Walters, K.L., and P.A. Glancy 1969 Reconnaissance of Geology and of Ground-Water Occurrence in Whitman County, Washington State of Washington, Department of Water Resources, Water Supply Bulletin No. 26 Warnick, C.C. 1971 Summary Comments on Moscow-Pullman Water Supply With Special Reference to the Advisability of Relying on Ground Water from the Presently Identified Ground Water Aquifers of the Moscow Basin Moscow City Hall Washington Department of Ecology 1988 Guidelines for Development of Ground Water Management Areas and Programs Washington Department of Ecology, Chapter 173-100 WAC Waters, A.C. 1961 Stratigraphic and Lithologic variations in Columbia River Basalt American Journal of Science Watershed Science

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2006 Airborne Thermal Infrared Remote Sensing Palouse River Basin, WA/ID Washington Department of Ecology Webster, G.D. 1979 Surficial Geologic Map of the Pullman Quad, Washington. Washington Department of Natural Resources Western Consultants, Inc. 1973 Engineer Report and Master Plan For Future Additions to Municipal Water System, Troy, Idaho Report for the City of Troy White, D.L. 1973 Lacustrine Deposit Near White Bird, Idaho ?? Abstracts with Programs North-Central Section, Columbia, Missouri Whiteman, K.J. 1986 Ground Water Levels in Three Basalt Hydrologic Units Underlying the Columbia Plateau, Washington and Oregon US Geological Survey Water Resources Investigation Report 86-4046 Whiteman, K.J., J.J. Vaccaro, J.B. Gonthier, and H.H. Bauer 1994 The Hydrogeologic Framework and Geochemistry of the Columbia Plateau Aquifer System, Washington, Oregon, and Idaho US Geological Survey Professional Paper 1413-B Williams, R.E., and D.W. Allman 1969 Factors Affecting Infiltration and Recharge in a Loess Covered Basin Journal of Hydrology, Vol. 8, pp. 265-281 Williams, R.E., D.D. Eier, and A.T. Wallace 1969 Feasibility of Re-Use of Treated Wastewater for Irrigation, Fertilization and Ground-Water Recharge in Idaho Idaho Bureau of Mines and Geology, Pamphlet 143 Wyatt-Jaykim Engineers and D.R. Ralston 1987 Construction Report for the WSU No. 7 Production/Test Well Wyatt-Jaykim Engineers and D.R. Ralston

* Document not included in database

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