<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 />
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