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<br />C01GvU <br /> <br />U.S. Bureau of Census (1970, 1980, 1990), and average number of persons per household by area <br />as well as other census information is available from the U.S. Department of Commerce (1991). <br />Average depth of withdrawal can be estimated in particular areas using well-completion records <br />(New Mexico State Engineer Office files, Albuquerque). . <br /> <br />Santa Fe Group Aquifer System <br /> <br />Water removed from storage in the Santa Fe Group aquifer system in the Albuquerque area <br />is a source of water to the flow system. Withdrawal of ground water from storage in the <br />Albuquerque area was estimated using the Kernodle and others (1995) model to be about 72,000 <br />acre-feet for the year ending in March 1994. This volume is about 46 percent of the 157,000 acre- <br />feet per year withdrawn by wells in the Albuquerque area. Because withdrawal from storage is <br />a large component of the water budget, documenting changes in the volume of water in storage <br />in relation to the volume withdrawn is essential. Essential information needed to document <br />changes in storage are the hydraulic-head and aquifer-compaction measurements described <br />previously (see" Aquifer storage" section of this report) and measurements that would indicate <br />changes in aquifer storage, such as measurement of hydraulic heads in piezometers and <br />temporal gravity surveys (discussed in the "Plan of study" section of this report). <br /> <br />Ground water moving into the Albuquerque area from other parts of the aquifer system is <br />also a source of water to the flow system. Based on the Kernodle and others (1995) model this <br />was estimated to be about 20,000 acre-feet for the year ending in March 1994. Yapp (1985) and <br />Logan (1990) have used ground-water-chemistry information, including environmental isotopes, <br />to identify possible pathways for ground-water flow within and into the Albuquerque area. <br />Continuing the collection of information on the chemical composition (including environmental <br />isotope concentrations) of ground water in various parts of the aquifer would be useful, <br />particularly if this information is collected from the proposed additional observation wells <br />described previously. These observation wells would enable water-sample collection from <br />particular depths in the aquifer, which would provide information on changes in chemical <br />composition vertically within the aquifer. Many ground-water samples collected previously <br />have been from production wells and are, therefore, composite samples over a vertical section of <br />the aquifer. Existing and additional ground-water chemical analyses would then be useful in <br />conceptualizing the ground-water flow system and in refining a ground-water-flow model of the <br />Albuquerque Basin. <br /> <br />Rio Grande, Canal, and Drain Seepage <br /> <br />Rio Grande and canal seepage to the aquifer system in the Albuquerque area was <br />estimated by Kernodle and others (1995) to be about 79,000 acre-feet for the year ending in <br />March 1994, and seepage from the aquifer to the drains was estimated to be about 43,000 acre- <br />feet for the year ending in March 1994. The estimated net seepage from the Rio Grande surface- <br />water system to the aquifer system was 36,000 acre-feet per year (79,000 minus 43,000), or about <br />23 percent of the withdrawal by wells. <br /> <br />Seepage between the Rio Grande, canals and drains, and the aquifer system has been <br />estimated by the Bureau of Reclamation in various investigations. Hansen (in press) estimated <br />that 33,000 acre-feet of water per year seeps from the Rio Grande channel and riverside drain <br />system to the aquifer system and about 34,000 acre-feet per year seeps from the canals and <br />applied irrigation water to the aquifer system between Bernalillo and Isleta Pueblo. Gould and <br />Hansen (1994, p. 17-18) calculated seepage rates for five selected canals in the Albuquerque area <br />to average from 0.38 to 0.42 foot per day at normal water-surface elevations and from 0.21 to 0.22 <br />foot per day below normal water-surface elevations. The water table was below the bottom of <br /> <br />24 <br />