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<br /> <br />significant ground-water input to a stream, such as from <br />springs, Radon also has been used to determine stream- <br />water movement to ground water. For example, radon was <br />used in a study in France to determine stream-water loss to <br />ground water as a result of ground-water withdrawals, (See <br />Figure G-2,) <br />An example of using stream-water temperature and <br />sediment temperature for mapping gaining and losing reaches <br />of a stream is shown in Figure G-3, In gaining reaches of the <br />stream, sediment temperature and stream-water temperature <br />are markedly different. In losing reaches of the stream, the <br />diurnal fluctuations of ternpelature in the stleam are reflected <br />more strongly in the sediment temperature, <br /> <br /> <br />Pumping well <br /> <br />Lot River <br /> <br /> <br />,_ Water table <br />~-------------==::: <br /> <br />---~-- <br /> <br />,.------------ <br /> <br />_ Ground- <br />water <br />flow <br /> <br />Chemically Mixing zone <br />reducing <br />Riller zone Alluvial aquifer <br />I I <br />I I <br />I I Dissolved oxygen <br /> <br />~ <br />~ <br /> <br />I I <br /> <br />-/LI: <br /> <br />I Manganese <br />I I <br />I <br />I I <br /> <br />-N Zl,e <br />I <br />I <br />I <br />I Dissolved organic carbon <br /> <br />Radon <br /> <br /> <br />specific conductance <br /> <br />Figure G-2, Sharp changes in chemical concentrations <br />were detected over short distances as water from the Lot <br />River in France moved into its contiguous alluvial aquifer in <br />response to pumping from a well, Specific conductance of <br />water was used as an environmental tracer to determine the <br />extent of mixing of surface water with ground water, and <br />radon was used to determine the inflow rate of stream water, <br />Both pieces of information were then used to calculate the <br />rate at which dissolved metals reacted to form solid phases <br />during movement of stream water toward the pumping well, <br />(Modified from Bourg, A.C,M" and Bertin, C" 1993, <br />Biogeochemical processes during the infiltration of river <br />water into an alluvial aquifer: Env;ronmental Science and <br />Technology, v, 27, p, 661-666,) (Reprinted with permission <br />from the American Chemical Society,) <br /> <br /> <br /> <br />Sampling for a chemical tracer. (Photograph by <br />Gary Zellweger.) <br /> <br /> 75 <br /> A <br /> 70 <br /> 65 <br />.... <br />~60 <br />Z <br />w <br />a; <br />:I: 55 <br />;1 <br /><J) <br />w <br />~50 <br /><-' 246 248 <br />w <br />a <br />~ 76 <br />W B <br />a; 7. <br />:> <br />.... <br />~72 <br />w <br />"- <br />~ 70 <br />.... <br /> 68 <br /> 66 <br /> <br />Gaining Reach <br /> <br />-Water column <br /> <br /> <br />\ <br />Sediment <br /> <br />250 252 254 256 258 260 <br /> <br />Losi ng Reach <br /> <br />-Water <br />column <br /> <br /> <br />64 <br /> <br />62 <br />218 220 222 224 226 228 230 232 234 236 <br />DAY OF YEAR <br /> <br />Ffgure G-3. Ground-water temperatures <br />generally are more stable than surface-water <br />temperatures, Therefore, gaining reaches of <br />Juday Creek in Indiana are characterized <br />by relatively stable sediment temperatures <br />compared to stream-water temperatures (A), <br />Conversely, losing reaches are characterized <br />by more variable sediment temperatures caused <br />by the temperature of the inflowing surface <br />water (B), (Modified from Silliman, S.E., and <br />Booth, OF" 1993, Analysis of time series <br />measurements of sediment temperature for <br />identification of gaining versus losing portions <br />of Juday Creek, Indiana: Journal of Hydrology, <br />v, 146, p, 131-148.) (Reprinted with permission <br />from Elsevier Science-NL, Amsterdam, The <br />Netherlands.) <br /> <br />31 <br />