Discharge.--
<br />PLATTE RIVER BASIN
<br />06724000 SAINT VRAIN CREEK AT LYONS, CO
<br />Location.--
<br />Drainage and Period of Record.--
<br />Lat. 40°13'05",Long. 105°15'34", in NW¼NW¼ sec. 20, T.3 N,, R.70 W., Boulder County, Hydrologic Unit 10190005, on left
<br />bank 75 ft southwest of U.S. Highway 36 (State Highways 7 and 66) at southeast edge of Lyons, 400 ft upstream from St.
<br />Vrain Supply Canal, and 0.4 mi downstream from confluence of North and South St. Vrain Creeks.
<br />212 mi². Aug. 1887 to Sep. 1891, June 1895 to current year. Monthly only data for some periods. Water quality
<br />data available from Oct. 1977 to Feb. 1981. On March 23, 2003, the gage was moved approximately 0.2 mi
<br />upstream. In the new location, the gage is above the Supply Ditch diversion, whereas the old location was below
<br />this diversion.
<br />Graphical water stage recorder and an incremental shaft encoder connected to a high data rate Data Collection Platform
<br />(DCP) in a 6-foot by 6-foot wooden shelter* with 42-inch precast concrete stilling well upstream of a low head concrete
<br />diversion dam. An Electric Tape Gage (ETG) located on the instrument shelf is the primary reference with a supplementary
<br />cantilever chain gage located 10 feet downstream of the shelter. The stilling well is connected to the channel via four 2-inch
<br />inlets, three of which are equipped with valves and flushing equipment. A secondary shaft encoder is installed on the
<br />instrument shelf of the shelter. This shaft encoder is used for the Highland Ditch Company’s Supervisory Control and Data
<br />Acquisition (SCADA) system. This instrument is maintained by the Colorado Division of Water Resources (DWR) and
<br />operated such that the instruments stage reading is set to the base gage stage plus or minus last measured shift. *On May
<br />27, 2009 the timber shelter was replaced with a 6-foot by 6-foot exposed aggregate precast concrete building .
<br />Equipment.--
<br />Hydrographic Conditions.--
<br />Gage-Height Record.--
<br />Datum Corrections.--
<br />Rating.--
<br />Discharge.--
<br />216 square miles of drainage from USGS topographic maps; mainly comprised of forested and grassy areas with varying
<br />topography. Gage is located below the confluence of the south and north forks of the Saint Vrain and below most of Lyons
<br />Colorado. Beaver Creek and Button Rock Reservoirs are upstream of this gage as well as numerous other diversions of
<br />varying magnitude. This station is susceptible to rapid increases in stage due to storm runoff events from hardened
<br />surfaces within the Town of Lyons, CO.
<br />The primary record is hourly averages of telemetered 15-minute data with chart record as backup. Frequent visits show
<br />good agreement between primary and backup records, and the ETG. No flush corrections or inlet plugging events occurred
<br />this year. However, debris accumulation on the diversion dam was a problem. Accumulated debris was removed from the
<br />control on April 6, 2009 resulting in a -0.02 foot change to the gage-height. Otherwise, the gage-height record is complete
<br />and reliable except: December 4,5 and 10-13, 2008, February 28, 2009, March 1, March 11-14 and 26-28, 2009, when ice
<br />affected the stage-discharge relationship; May 27, 2009, when the gage was offline for 14 hours for shelter replacement
<br />and no gage-height information available; and June 3 to 23, 2009, when there was debris accumulation on control,
<br />unspecified date debris was accumulated and shed. The gage was closed for the winter from December 14, 2008 to
<br />February 25, 2009.
<br />Prior to the shelter replacement, levels were last run on September 22, 2006 and found to be within allowable tolerances.
<br /> Levels were run on May 28 on the new shelter. At that time the gage datum was misinterpreted and the gage was set to
<br />read 1.08 ft higher than previously. Levels were run again on September 22, and the gage was found to be reading 1.09 ft
<br />high. A correction of -1.09 ft. correction was applied to the record and measurement GH’s from the June 8 measurement
<br />to the time of the correction on September 22. A correction of -1.08 ft. was applied to the May 28 record and measurement
<br />GH. Between May 28 and June 8, the correction was prorated from -1.08 to -1.09 ft. The 0.01 ft difference was
<br />presumed to be due to settling of the shelter on the sealer used between the shelter and the floor. The gage datum was
<br />restored to 5301.080 feet following the September 3, 2009 levels circuit.
<br />The control for low to mid level stages is a low-head concrete diversion dam for the Supply Ditch approximately 570 feet
<br />below the gage. At higher stages the gage reverts to channel control; which, has not been fully defined since the gage was
<br />relocated in 2003. The diversion dam and ditch check structure approximately 1000 feet below the gage can gather debris
<br />and cause back water conditions at the gage under certain operational circumstances. Fill and scour conditions as well as
<br />debris accumulation on the low water control contributed to shifting away from the rating. Rating No. 25 in use since
<br />October 1, 2007 is defined by measurements from 11.8 to 976 cubic feet per second (cfs). Twenty-five measurements
<br />(Nos. 549-573) were performed this water year ranging in discharge from 21.1 to 758 cfs. Six measurements (Nos. 561-
<br />564, 566, 567) were performed with a Teledyne RD Instruments StreamPro Acoustic Doppler Current Profiler (ADCP).
<br /> Measurements made this water year cover the range in stage experienced this year well. The peak discharge of 890 cfs
<br />occurred at 0515 June 27, 2009 at a gage height of 3.45 feet (datum correction of -1.09 feet applied) with a shift of -0.05 ft.
<br />It exceed the stage of Measurement No. 566 by 0.41 ft.
<br />Shifting control method was used this year. Unadjusted shifts ranged from 0.06 to -0.09 feet. Shifts were applied as
<br />follows: October 1 through December 14, 2008: time dependent shifting as defined by Msmt. Nos. 548-551; February 25
<br />through April 21, 2009: time dependent shifting as defined by Msmt. Nos. 555-557; April 21 through June 3, 2009: stage
<br />dependent shifting utilizing variable shift table SVCLYOCOVS09-01, which is based of nine measurements (Nos. 557-560,
<br />564-567). Nos. 557-560 were performed during the period of use and Nos. 564-567 were performed following the period
<br />of use but were evaluated to better define the upper regions of the table during the period June 3 through June 23, 2009.
<br />Time dependent shifting as defined by Msmt. Nos. 560-564. Nos. 561-563 were performed on June 8, 2009 using the
<br />ADCP instrument. Nos. 561 and 562 were adjusted 1% and -2% to a measurement series mean shift of +0.05 feet. The
<br />measurements verified a relatively large positive shift change from the preceding and following measurements and
<br />associated stage-shift tables. This shift was conjectured to be due to siphonic action at the control, possibly involving light
<br />debris accumulation between the May 28 and June 23 measurements. June 3 was taken to be the end point for the
<br />previous table and the beginning of time shifting to the June 8 measurement shifts, since June 3 saw a significant stage
<br />rise. June 23 through September 18, 2009; stage dependent shifting utilizing variable shift table SVCLYOCOVS09-02,
<br />which is based on ten measurements (Nos. 564-573) made during the period of use. Nos. 564, 565, 567, 568, 571 were
<br />adjusted 15, -5%, 4%, -1% and -2% respectively to better fit the shift distribution September 18 through the end of the
<br />water year: time dependent shifting as defined by Msmt. Nos. 573-574 .
<br />2009Water Year
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