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<br /> <br /> 9,3 <br /> 9,2 <br /> 9,1 <br />en <br />I- 9,0 <br />Z <br />::J <br />ci <br />a: 8,9 <br /><( <br />Cl <br />Z <br />~ 8,8 <br />en <br />~ <br />:C 8,7 <br />c. <br /> 8,6 <br /> 8,5 <br /> <br />--.-- <br />,,0. <br />-~- <br /> <br />Measured pH <br />Simulated pH at equilibrium with atmospheric carbon dioxide <br />Simulated pH at equilibrium with atmospheric carbon dioxide and calcite <br />Note: number by symbol is site number in tables 1 and 3 <br /> <br />6 <br />"'....-............ <br />//// -----____ 8 9 11 <br />-..----------11I0",,,,,,,,,,,12 <br />8 1/ <br />/" ..0."""'" ';P, <br />.. I <br />I <br />I <br />I / <br />\ -",- <br />\ _..-....-- <br />11./- <br />8 9 <br />6_--------~------A~~------~ <br /> <br />.3 <br />II <br />" <br />" <br />II <br />I I <br />I I <br />I I <br />I I <br />I I <br />I I <br />I I <br />I I <br />I I <br />I I <br />I I <br />I I <br />I I <br />I I <br />I I <br />I I <br />I I <br />I I <br />I I <br />I I <br />I \.._-- <br />: 3 11I/ <br />", I.Q 5 <br />2C:P 'o" <br />I <br />. <br />/ 2 <br />, <br />~ // <br />.../' 3... <br />_" ...............2 .JIfII&-, <br />1 -........, <br /> <br />1 <br /> <br />Q,,\ <br /> <br />\ 5",..,,0'" <br />0' <br /> <br />8.4 <br />230 220 <br /> <br /> <br />12 <br /> <br />120 <br /> <br />40 <br /> <br />o <br /> <br />200 <br /> <br />180 <br /> <br />160 <br /> <br />140 <br /> <br />DISTANCE FROM MOUTH OF YAMPA RIVER, IN RIVER MILES <br /> <br />20 <br /> <br />100 <br /> <br />80 <br /> <br />60 <br /> <br />Figure 6, Measured and simulated pH at Yampa River sites, August 16-19,1999, <br /> <br />Furth(lr hypothetical simulations using <br />PHREEQC to allow samples collected from Yampa <br />River sites tq precipitate enough calcite to attain equi- <br />librium with that mineral further decreased pH values <br />between 0,13 and 0,31 unit (compared to pH at equi- <br />librium with atmospheric Peo ) (fig, 6), These simula- <br />tions indicate that pH for Yam~a River water would be <br />restricted to the narrow range from 8,42 to 8,50 if it <br />was in equilibrium with calcite and atmospheric CO2, <br /> <br />Diurnal Measurements <br /> <br />Measurements at Yampa River above Elk River <br />(site 3 in fig, 1) during August 23-24, 1999, indicated <br />strong diurnal fluctuations in pH and dissolved oxygen <br />concentration (fig, 7) as a result of dominance by <br />photosynthesis during daylight and by respiration plus <br />oxidation ofiorganic matter during night. Values for <br />pH ranged from a peak of 9,07 at 1500 hours in the <br />afternoon of August 23 to a minimum of 7,92 at <br />0300 hours the next morning (a diurnal change of <br />LIS units), Dissolved oxygen concentrations peaked <br />at 178 percent of saturation at the same time pH <br />peaked and attained a minimum of 66 percent of satu- <br />ration at the time of minimum pH, (Because the degree <br />of saturation of dissolved oxygen is dependent on <br /> <br />water temperature, minimum and maximum concen- <br />tration of dissolved oxygen does not exactly corre- <br />spond to minimum and maximum concentration,) <br />Specific conductance remained relatively constant at <br />331 to 343 J,lS/cm over the 23-hour period, The abrupt <br />decrease in pH value from 9,07 at 1500 hours to 8,84 <br />at 1600 hours apparently was caused by a IS-minute <br />cloudy period between those measurements; this <br />temporary inhibition of photosynthesis probably <br />prevented pH from reaching its maximum potential <br />that afternoon at this site, a conclusion supported by a <br />pH of 9.20 at 1600 hours on August 18, 1999, <br /> <br />Diurnal measurements at Yampa River below <br />Craig (site 6 in fig, 1) during August 23-24, 1999 <br />(fig, 8) also indicated substantial effects of photosyn- <br />thesis and respiration plus oxidation of organic matter, <br />although not as strongly as at Yampa River above <br />Elk River, Values for pH peaked at 8,78 at 1800 hours <br />on August 23 and attained a minimum of 8,17 at <br />0600 hours the next day (a diurnal change of 0,61 <br />unit), Dissolved oxygen concentration peaked at 140 <br />percent of saturation at 1600 hours on August 23 and <br />attained a minimum of 78 percent of saturation at <br />0600 hours the next day, Specific conductance ranged <br />from 346 to 380 IlS/cm, <br /> <br />12 Evaluatio~ of Trends in pH in the Vamps River, Northwestern Colorado, 1950-2000 <br />