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TECHNICAL MEMORANDUM <br />AmerAlia, Inc. <br />October 19, 1999 <br />Page 4 <br />the two aquifers and is up to 200 feet thick. Later studies redefined the bedrock aquifer system to <br />include the upper aquifer as defined in earlier studies, the lower aquifer as the zone between the <br />Mahogany zone and L-5 zone, and the Dissolution Surface. The thickness of the lower aquifer is about <br />30D feet. The primary water-bearing zones in the upper and lower aquifers are the "A Groove" and "B <br />Groove" respectively. The "A Groove" is located directly above the Mahogany zone, with a thickness of <br />about 15 feet. The "B Groove" is located directly below the Mahogany zone with a thickness of about 20 <br />feet. The strata immediately above the Dissolution Surface is a significant water-bearing zone above the <br />saline portion of the Parachute Creek member (zones R-5 to R-2) and is part of the tower aquifer. <br />However, based on limited water quality data, the water quality of the strata immediately above the <br />Dissolution Surface does not meet the drinking, agricultural, livestock, or wildlife water quality <br />standards, because of its elevated levels of TDS and other constituents. A general hydrostratigraphic <br />column for the Project area is shown on Figure 2. <br />2.2 Existing Data <br />A large amount of water quality information is available for wells from the WRN site. Data from one <br />well in the A-Groove section of the upper aquifer, four wells in the B-Groove section of the lower <br />aquifer, and two wells in the Dissolution Surface zone have been analyzed. Several of these wells have <br />been sampled monthly for a large number of constituents since 1989. A presentation of median and first <br />and third quartile has been selected to summarize the White River Nahcolite data in Table 1. This has <br />the advantage of being more resistant towards outliers. The data has been analyzed initially and it was <br />found that the data is fairly consistent except for some outliers. These outliers have a large influence on <br />the mean, but little influence on the median (Helsel and Hirsch, 1992). The spread of data can also be <br />better estimated by the interquartile range, as it measures the range of the central 50 percent of data and <br />is not influenced by the 25 percent on either end (Helsel and Hirsch, 1992). Some electronic data is <br />available on wells from the C-a Tract. Data exists for bedrock wells GS-2M, GS-3M and GS-SM, and <br />alluvial wells 522, 524, and 528. The data available is generally annual mean values for selected <br />components for the some years between 1975 and 1985. Two USGS wells exist on the Project site (TH <br />75-7A and 7B), and water quality data exist for samples collected in 1975. A short summary of the data <br />is presented in Table 1, and a summary for each well is presented in Appendix A. <br />2ndFinalTecMicalMemodoc 10/19/99 TRC HYDRO-GEO CONSULTANTS <br />