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<br />. <br />.- <br /> <br />4 Losses and Gains for Eight Unlined Canals Along the Purgatoire River near Trinidad, Colorado, 200ll-2llll4 <br /> <br />2-mile reach (located from about 1.5 miles to 3.5 miles down- <br />stream from the Picketwire headgate) of Picketwire Canal and <br />deliver water directly to Baca lands. <br />El Mora Canal water is delivered through a single lat- <br />eral turnout from the Picketwire Canal, measured through a <br />Parshall flume, and then distributed through a discrete ditch <br />to the EI Moro lands. Similarly, the John Rood Canal water is <br />diverted at the Model Canal head gate, carried in Model Canal <br />about 1.5 miles, and then diverted into John Flood Canal <br />through a turnout from Model Canal. The John Rood Canal <br />water is measured using a Parshall flume and then distributed <br />to John Flood lands (fig. I). <br /> <br />Acknowledgments <br /> <br />The author wishes to thank many landowners within <br />the study area for allowing access to their property to make <br />discharge measurements along the canals. In addition, the <br />author would like to thank Thelma Lujan from the Purgatoire <br />River Water Conservancy District for her assistance in <br />coordinating site visits and providing contact information <br />and Danny Marques from the Colorado Division of Water <br />Resources for providing detailed information on the operation <br />of the canal system and answering many questions. <br /> <br />Methods for Loss and Gain <br />Investigations <br /> <br />Field reconnaissance of diversion structures and loca- <br />tion of measurement sites, discharge measurements, and loss <br />and gain computations are discussed in this section of the <br />report. <br /> <br />Field Reconnaissance <br /> <br />Field reconnaissance was conducted to locate divcrsion <br />structures, select measurement locations, and arrange access <br />to sites. All diversion structures along each main canal were <br />located, and their latitude and longitude coordinates were <br />determined using a global positioning system (table I). <br />Parshall flumes used to measure inigation diversion <br />at the canal headgates ranged in size from 9 inches (9-ft3/S <br />free-flow capacity) to 10 feet (300.ft3/S free.tlow capacity). <br />Figure 2 shows a photograph of the water-stage recorder <br />and Parshall tlume at Ihc Hoehne Canal headgate (HOHG). <br />Lateral turnouts with Parshall tlumes and (or) splitter boxes <br />are used to measure and divert water out of the main canal to <br />shareholders along the L:anal for irrigation. Figure 3 shows <br />an example of a splitter box located at site SS07 on Enlarged <br />Southside Canal. <br /> <br />Discharge Measurements <br /> <br /> <br />Discharge measurements were made along the eight <br />canals during steady-state conditions to identify subreaches <br />with losses or gains. Steady-state conditions were defined as <br />periods with little or no precipitation and stable canal inflows <br />at the headgates for at least 4 to 7 days before measurements <br />were made. Inflows were considered stable if flow did not vary <br />by more than 5 percent at the canal headgates. Discharge mea- <br />surements were made at main canal and lateral diversion sites <br />using either an Acoustic Doppler Current Meter (ADCP) or a <br />vertical-axis mechanical current meter. The ADCP measurc- <br />ments were made following methods described by Simpson <br />and Oltmann (1993). Vertical-axis current-meter measure- <br />ments were made following methods described by Rantz and <br />others (1982). <br />The accuracy of a discharge measurement is affected by <br />various factors such as condition of measuring equipment, <br />characteristics of the measurcment section, spacing of obser- <br />vation verticals, changing stage, measurement of depth and <br />velocity, and other factors. Four accuracy classifications are <br />used by the USGS to rate discharge measurements. A mea- <br />surement rated excellent means that the measured discharge is <br />probably within 2 percent of the true discharge; good, within <br />5 percent; fair, within 8 percent; and a measurement rated poor <br />may be more than 8 percent different from the true discharge <br />(Rantz and others, 1982). The accuracy classification of a dis- <br />charge measurement is a somewhat subjective evaluation made <br />by the field technician making. the measurement. The tield <br />technician considers characteristics of the measurement sec- <br />tion (type of channel bottom, flow distribution, and so forth), <br />instrument performance, and other factors and then assigns a <br />rating to the measurement. <br />Discharge measurements made during this study were <br />generally rated good or fair, and a small number of measure- <br />ments were rated poor. Because of measurement uncertainty, a <br />single pair of measurements may not be sufficient to determine <br />if a loss or gain occurs in a subreach. Measured losses or gains <br />must be greater in magnitude than the uncertainty associ- <br />ated with the measurement to be considered meaningful. The <br />uncertainty of a measurement is calculated on the basis of the <br />measurement rating. For example, a measurement of 20 ft3/s <br />with a rating of good has an assumed uncertainty of 5 percent, <br />or ;t 1 ft3jS. Therefore, a loss or gain must be greater than 1 ft3/S <br />to be considered meaningful. <br />Discharge measurements began at the headgate flume <br />in the main canal and were repeated, moving downstream, at <br />multiple locations in the main canal. generally during a I-day <br />period. Discharge measurements were made over several <br />days along Enlarged Southside Canal due to the canal length <br />and number of measurement sites. When it was necessary to <br />extend loss and gain discharge measurements in a canal over <br />more than one day, the last site measured in the main canal <br />