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<br />Continuous data from the monitoring stations <br />were supported by monthly site visits during the <br />open-water season, and bi-monthly visits when ice <br />cover was present. Field measurements of streamflow <br />were made using the cUrrent-meter method (Buchanan <br />and Somers. 1969), The calibration of the water- <br />quality monitor was checked using field meters and <br />standard solutions prepared according to standard <br />procedures (R.W, Boulger. U,S. Geological Survey. <br />unpub, data, 1989). Data from these visits were <br />used to analyze and compute the continuous data <br />from the monitoring stations according to standard <br />procedures (Rantz and others. 1982; Kennedy, 1983; <br />R.W. Boulger. U.S. Geological Survey, unpub. data, <br />1989), <br />Seven water-quality samples were collected <br />during rain or turbidity events. An event is a rise <br />in streamflow or an increase in turbidity due to a <br />rainstorm. Field measurements of specific conduc- <br />tance, water temperature, dissolved oxygen, and <br />barometric pressure were made at streamside <br />(M.A. Sylvester and others, U.S. Geological Survey, <br />unpub. data, 1990). Turbidity and pH were measured <br />from samples taken from the churn splitter. Samples <br />for inorganic analysis were collected by equal-width- <br />increment (EWI) or equal-discharge-increment <br />(EDl) methods using a DH-SI polyethylene <br />isokinetic sampler and split for separate analyses <br />with a USGS churn splitter (Ward and Harr, 1990). <br />Samples requiring filtered water were filtered by using <br />a peristaltic pump and disposable 0.45-mm capsule <br />filters in an enclosed filter chamber. Trace-element <br />samples were preserved as necessary with ultrapure <br />nitric acid or nitric acid and potassium dichromate <br />(for mercury samples). Nutrient samples were chilled <br />to less than 40C. <br />Samples of suspended sediment were collected <br />by EWI or EDl methods with a DH-48 hand sampler <br />or DH-59 cable sampler (Guy and Norman, 1970) <br />and by the use of an automatic pumping sampler with <br />a fixed intake point (Edwards and Glysson, 1988). <br />Samples were collected for analyses of concentration <br />and percent finer than 0.062-mm. Multiple daily <br />samples were collected with the pumping sampler for <br />daily sediment load computations; however, those data <br />are not included in this report. <br /> <br />Hlgh- and Low-Streamflow <br />Water-Quality Sampling <br /> <br />A synoptic stream sampling design was <br />used to compare high- and low-streamflow regimes <br />among sites. The term "synoptic" is used to refer to <br />samples taken at approximately the same time of <br />year. The sampling sites are listed in table 3 and <br />shown in figure 3. A high-flow sample was collected <br />at 21 of the sites in mid-June. A low-flow sample was <br />collected at all 23 sites in early September. Instanta- <br />neous streamflow was measured by the current- <br />meter method (Buchanan and Somers, 1969). Field <br />measurements of specific conductance, water tempera- <br />ture. dissolved oxygen. and barometric pressure were <br />made at streamside (M.A. Sylvester and others, <br />U,S. Geological Survey, unpub. data, 1990). Turbidity <br />and pH were measured from samples taken from the <br />churn splitter. Samples for inorganic analysis were <br />collected by EWI or EDl methods using a DH-SI <br />polyethylene isokinetic sampler and split for separate <br />analyses with a USGS churn splitter (Ward and Harr, <br />1990). Samples requiring filtered water were filtered <br />by using a peristaltic pump and disposable 0.45-J.lm <br />capsule filters in an enclosed filter chamber. Trace- <br />element samples were preserved as necessary with <br />ultrapure nitric acid or nitric acid and potassium <br />dichromate (for mercury samples). Nutrient samples <br />were chilled to less than 40C. <br />Samples for organic analysis were collected <br />in a baked glass bottle by EWI, EDl, or dip methods, <br />The total organic carbon sample was not filtered, <br />whereas the dissolved organic carbon samples were <br />filtered through a 0.45-J.lm silver filter. Carbon <br />samples were chilled to less than 40C until analyzed. <br />Suspended-sediment samples also were <br />collected by EWI or EDl methods using appropriate <br />hand- or cable-operated isokinetic samplers (Edwards <br />and Glysson, 1988). Samples were collected for <br />suspended-sediment concentration and percentage <br />of particles finer than 0.062 mm using standard <br />techniques (Guy. 1969). <br /> <br />Road-Runoff Sampling <br /> <br />Road runoff in shoulder ditches and cross drains <br />was sampled from paved and unpaved sections of <br />the Guanella Pass road. The sites sampled are listed <br /> <br />8 HydrologIc and Water.Quallty Da'a, Guanella Paa. Area, Colorado, Watar Vea, 1995 <br />