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GROUNDWATER RESIDENCE Thm AND RECHARGE TEMPERATURE ESTIMATES OF THE DENVER AND ARAPAHOE AQULFms, DENVER BASIN, COLORADO <br />Recharge Temperature <br />The temperature of recharging groundwater, an approxi- <br />mation of mean - annual air temperature, can be estimated <br />from concentrations of atmospheric noble gases dissolved <br />in groundwater using the general temperature -gas solubil- <br />ity relationship, Henry's Law (e.g., Stute et al., 1992; <br />Aeschbach -Hertig et al., 1999). The concentrations of inert <br />gases in groundwater result from the temperature- and <br />pressure (elevation)- dependent equilibration of water with <br />the atmosphere, plus the addition of excess air arising <br />from dissolution of entrained air bubbles below the water <br />table (Stute and Schlosser, 2000). The excess air may be <br />fractionated due to partial dissolution or re- equilibration of <br />the gas (Aeschbach -Hertig et al., 1999). <br />Variation in paleotemperatures estimated from concen- <br />trations of noble gases suggests a temperature suppression <br />ranging from 5 -9 °C during the last glacial period <br />(Aeschbach - Hertig et al., 2000). Noble gas temperatures in <br />the south - central and southwestern U.S. during the last <br />glacial period were approximately 5 °C cooler than <br />Holocene temperatures (Stute et al., 1992; Clark et al., <br />1998), consistent with other estimates of continental tem- <br />perature change and local glacial - climate reconstructions <br />(Muhs et al., 1999). <br />METHODS <br />Sampling <br />Six samples were collected from locations that lie along <br />a transect parallel to the presumed modern groundwater <br />flow path beginning near the southern outcrop of the <br />aquifers (Fig. 1). The samples were collected from ground- <br />water of the Arapahoe and Denver aquifers near Parker, <br />Colorado during the spring of 2002 and near Aurora and <br />Donala (near Colorado Springs), Colorado during the <br />spring of 2003 (Table 1). One -liter water samples were <br />analyzed for dissolved inorganic carbon (DIC) isotopes by <br />atomic mass - spectrometry at Beta Analytical Labs. Results <br />of DIC analysis are reported in percent modern carbon <br />(pmQ for 14C and delta 13- carbon per mil VPDB (813C %o) <br />for relative 13C /12C. Samples for dissolved gas analyses <br />were collected following the protocol outlined by Manning <br />et al. (2003) and were analyzed by the Noble Gas Labora- <br />tory at the University of Utah for 28N2 3202, 20Ne, 40Ar, <br />84Kr, 3He and 4He. Results of the dissolved gas analysis are <br />reported in molar- fraction (unit -less) and precision of mea- <br />surements is a few percent. Additional field measurements <br />of temperature (T) and total dissolved gas pressure (PTDG) <br />of the groundwater were made. A detailed description of <br />the sampling procedure and analysis may be found in <br />Novotny (2004). <br />A 0 5 10 20 3(� <br />files <br />Denve <br />UR -07 <br />CAAUR -08 <br />PARK-01 <br />�P <br />PIN-02 <br />LEGEND` <br />O Sample Location <br />Aquifer Outcrop -20N-04 <br />Urban Area <br />Increments f 1 Surface: <br />Increments of 100 ft from <br />high (dark) to low (light) <br />surface contour Colorado Springs <br />Figure 1. General locations of groundwater samples with 1978 <br />potentiometric surface of Arapahoe aquifer (Robson, 1987) for <br />reference. <br />Carbon -14 Activity Dilution and Determination of <br />Residence Time <br />Additional sources of carbon exist in most aquifers and <br />can cause dilution of the 14C activity. Therefore, a correc- <br />tion for the interaction of these sources with groundwater <br />was applied prior to the calculation of residence time. Cor- <br />rection methods involving mass - balance of 13C/12C (e.g., <br />Pearson and Swarzenki, 1974) were not used; ratios of <br />these isotopes in the potential sources of carbon in the <br />aquifers and recharge area are not known and the infer- <br />ence of these from other information is unreliable. <br />Resources were unavailable for isotopic- exchange or reac- <br />tion path models, and so these methods were not used. A <br />non - site - specific, empirically- derived dilution quotient <br />equal to 0.85 of the initial groundwater sample activity was <br />used to correct the 14C activities (Vogel, 1970). While this <br />correction does not physically represent 14C dilution in the <br />aquifers, other research indicates that differences between <br />this simple, empirical correction and more sophisticated <br />approaches are not significant in the lower Tertiary <br />aquifers of the San Juan Basin (Phillips et al., 1989), a <br />hydrogeologic and hydrochemical setting similar to the <br />Arapahoe and Denver aquifers. <br />163 The Rocky Mountain Association of Geologists <br />