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<br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I: <br />Ii <br />I <br /> <br />study period. Seasonal water temperature fluctuations were greater <br /> <br />at Ouray than at upstream sites. Main river water temperatures will <br /> <br />likely decrease through the winter. <br /> <br />Dissolved oxygen. - Dissolved oxygen levels at three main river sites <br />generally exhibited the opposite pattern seen for water temperature <br />(fig. 4). Dissolved oxygen decreased to a low in early August, then <br />increased steadily to mid-November. Dissolved oxygen levels at down- <br />stream sites were usually lower than at upstream sites. The minimum <br />level of dissolved oxygen was 6.5 mg/L, at Ouray. The lower solubility <br />of oxygen in warmer water is apparent at the main river sites. There <br />appears to be a greater seasonal change for both temperature and dissolved <br />oxygen downstream at Ouray compared to upstream at Island Park. <br /> <br />pH. - pH was usually higher at Island Park than at Jensen or Ouray. <br />From June to early August pH at Ouray exceeded that at Jensen, but <br />by mid-August, pH at Jensen was greater than at Ouray, but less than <br />at Island Park (fig. 5). pH appeared to increase throughout the sampling <br />period, but decreased in mid-August. This may be in response to increased <br />flows. <br /> <br />Specific conductance. - Specific conductance at three main river sites <br />was initially low in June, and increased steadily to late September, <br />then decreased slightly (fig. 6). Except for late September, specific <br />conductance increased from Island Park downstream to Ouray, reflecting <br /> <br />13 <br />