<?xml version='1.0' encoding='UTF-8'?>
<metadata xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance">
  <idinfo>
    <citation>
      <citeinfo>
        <origin>Erwin, Susannah O</origin>
        <origin>Bulliner, Edward A</origin>
        <origin>Sansom, Brandon J</origin>
        <pubdate>20201216</pubdate>
        <title>2017 Yellowstone River Dye-Trace Experiment</title>
        <geoform>tabular digital data</geoform>
        <pubinfo>
          <pubplace>Reston, VA</pubplace>
          <publish>U.S. Geological Survey</publish>
        </pubinfo>
        <onlink>https://doi.org/10.5066/P9DDX4HL</onlink>
      </citeinfo>
    </citation>
    <descript>
      <abstract>Data consist of geolocation, temperature, turbidity, time, and dye concentrations collected at four downstream locations from Rhodamine WT dye injection point on Yellowstone River in June 2017</abstract>
      <purpose>Tracer data were collected to inform advection-dispersion models used to estimate drift of larval pallid sturgeon in the Yellowstone River. Data may be used to derive travel times associated with discharge and flow conditions encountered during period of measurement.</purpose>
    </descript>
    <timeperd>
      <timeinfo>
        <rngdates>
          <begdate>20170629</begdate>
          <enddate>20170630</enddate>
        </rngdates>
      </timeinfo>
      <current>ground condition</current>
    </timeperd>
    <status>
      <progress>Complete</progress>
      <update>None planned</update>
    </status>
    <spdom>
      <bounding>
        <westbc>-104.8837</westbc>
        <eastbc>-103.9444</eastbc>
        <northbc>47.7726</northbc>
        <southbc>46.9934</southbc>
      </bounding>
      <descgeog>Yellowstone River from approximately Glendive, Montana to Sidney, Montana</descgeog>
    </spdom>
    <keywords>
      <theme>
        <themekt>USGS Thesaurus</themekt>
        <themekey>Hydrology</themekey>
      </theme>
      <theme>
        <themekt>ISO 19115 Topic Category</themekt>
        <themekey>inlandWaters</themekey>
        <themekey>biota</themekey>
      </theme>
      <theme>
        <themekt>National Agricultural Library Thesaurus</themekt>
        <themekey>hydrodynamic dispersion</themekey>
      </theme>
      <theme>
        <themekt>None</themekt>
        <themekey>larval drift</themekey>
        <themekey>rhodamine</themekey>
        <themekey>RWT</themekey>
      </theme>
      <theme>
        <themekt>USGS Metadata Identifier</themekt>
        <themekey>USGS:5fda1cdad34e30b9123ce3bc</themekey>
      </theme>
      <place>
        <placekt>Geographic Names Information System</placekt>
        <placekey>Missouri River</placekey>
        <placekey>Yellowstone River</placekey>
        <placekey>Montanna</placekey>
      </place>
    </keywords>
    <accconst>None. Please see 'Distribution Info' for details.</accconst>
    <useconst>None. Users are advised to read the data set's metadata thoroughly to understand appropriate use and data limitations.</useconst>
    <ptcontac>
      <cntinfo>
        <cntperp>
          <cntper>Brandon J Sansom</cntper>
          <cntorg>U.S. Geological Survey, Columbia Environmental Research Center</cntorg>
        </cntperp>
        <cntpos>Research Engineer</cntpos>
        <cntaddr>
          <addrtype>mailing and physical</addrtype>
          <address>4200 New Haven Road</address>
          <city>Columbia</city>
          <state>MO</state>
          <postal>65201</postal>
          <country>US</country>
        </cntaddr>
        <cntvoice>573-8756-5399</cntvoice>
        <cntemail>bsansom@usgs.gov</cntemail>
      </cntinfo>
    </ptcontac>
    <datacred>USGS Ecosystems Mission Area, USACE, Missouri River Recovery Program</datacred>
    <crossref>
      <citeinfo>
        <origin>Susannah O. Erwin</origin>
        <origin>Edward A. Bulliner</origin>
        <origin>J. Craig Fischenich</origin>
        <origin>Robert B. Jacobson</origin>
        <origin>Patrick J. Braaten</origin>
        <origin>Aaron J. DeLonay</origin>
        <pubdate>20181023</pubdate>
        <title>Evaluating flow management as a strategy to recover an endangered sturgeon species in the Upper Missouri River, USA</title>
        <geoform>OTHER</geoform>
        <serinfo>
          <sername>River Research and Applications</sername>
          <issue>vol. 34, issue 10</issue>
        </serinfo>
        <pubinfo>
          <pubplace>n/a</pubplace>
          <publish>Wiley</publish>
        </pubinfo>
        <onlink>https://doi.org/10.1002/rra.3371</onlink>
      </citeinfo>
    </crossref>
    <crossref>
      <citeinfo>
        <origin>E. F. Hubbard</origin>
        <origin>F. A. Kilpatrick</origin>
        <origin>L. A. Martens</origin>
        <origin>J. F. Wilson, Jr</origin>
        <pubdate>1982</pubdate>
        <title>Measurement of time of travel and dispersion in streams by dye tracing</title>
        <geoform>OTHER</geoform>
        <pubinfo>
          <pubplace>n/a</pubplace>
          <publish>US Geological Survey</publish>
        </pubinfo>
        <onlink>https://doi.org/10.3133/twri03A9_1982</onlink>
      </citeinfo>
    </crossref>
    <crossref>
      <citeinfo>
        <origin>Peter M. McCarthy</origin>
        <pubdate>2009</pubdate>
        <title>Travel times, streamflow velocities, and dispersion rates in the Yellowstone River, Montana</title>
        <geoform>OTHER</geoform>
        <serinfo>
          <sername>Scientific Investigations Report</sername>
          <issue>2009-5261</issue>
        </serinfo>
        <pubinfo>
          <pubplace>Reston, VA</pubplace>
          <publish>U.S. Geological Survey</publish>
        </pubinfo>
        <onlink>https://pubs.usgs.gov/sir/2009/5261/</onlink>
      </citeinfo>
    </crossref>
    <crossref>
      <citeinfo>
        <origin>Natural Resources Conservation Service</origin>
        <pubdate>2013</pubdate>
        <title>National Agriculture Imagery Program (NAIP)</title>
        <geoform>raster digital data</geoform>
        <pubinfo>
          <pubplace>na</pubplace>
          <publish>U.S. Department of Agriculture</publish>
        </pubinfo>
        <onlink>https://gdg.sc.egov.usda.gov/</onlink>
      </citeinfo>
    </crossref>
    <taxonomy>
      <keywtax>
        <taxonkt>USGS Biocomplexity Thesaurus</taxonkt>
        <taxonkey>Fishes</taxonkey>
      </keywtax>
      <taxonsys>
        <classsys>
          <classcit>
            <citeinfo>
              <origin>Integrated Taxonomic Information System (ITIS)</origin>
              <pubdate>2020</pubdate>
              <title>Integrated Taxonomic Information System (ITIS)</title>
              <geoform>ONLINE_REFERENCE</geoform>
              <pubinfo>
                <pubplace>Washington, D.C.</pubplace>
                <publish>Integrated Taxonomic Information System (ITIS)</publish>
              </pubinfo>
              <onlink>http://itis.gov</onlink>
            </citeinfo>
          </classcit>
        </classsys>
        <ider>
          <cntinfo>
            <cntperp>
              <cntper>Brandon J Sansom</cntper>
              <cntorg>U.S. Geological Survey, Columbia Environmental Research Center</cntorg>
            </cntperp>
            <cntpos>Research Engineer</cntpos>
            <cntaddr>
              <addrtype>mailing and physical</addrtype>
              <address>4200 New Haven Road</address>
              <city>Columbia</city>
              <state>MO</state>
              <postal>65201</postal>
              <country>US</country>
            </cntaddr>
            <cntvoice>573-875-5399</cntvoice>
            <cntemail>bsansom@usgs.gov</cntemail>
          </cntinfo>
        </ider>
        <taxonpro>No fish were identified.  The experiment was conducted to inform advection-dispersion models used to estimate drift of larval pallid sturgeon</taxonpro>
        <taxoncom>No fish were identified.  The experiment was conducted to inform advection-dispersion models used to estimate drift of larval pallid sturgeon</taxoncom>
      </taxonsys>
      <taxongen>No fish were identified.  The experiment was conducted to inform advection-dispersion models used to estimate drift of larval pallid sturgeon</taxongen>
      <taxoncl>
        <taxonrn>Kingdom</taxonrn>
        <taxonrv>Animalia</taxonrv>
        <taxoncl>
          <taxonrn>Subkingdom</taxonrn>
          <taxonrv>Bilateria</taxonrv>
          <taxoncl>
            <taxonrn>Infrakingdom</taxonrn>
            <taxonrv>Deuterostomia</taxonrv>
            <taxoncl>
              <taxonrn>Phylum</taxonrn>
              <taxonrv>Chordata</taxonrv>
              <taxoncl>
                <taxonrn>Subphylum</taxonrn>
                <taxonrv>Vertebrata</taxonrv>
                <taxoncl>
                  <taxonrn>Infraphylum</taxonrn>
                  <taxonrv>Gnathostomata</taxonrv>
                  <taxoncl>
                    <taxonrn>Superclass</taxonrn>
                    <taxonrv>Actinopterygii</taxonrv>
                    <taxoncl>
                      <taxonrn>Class</taxonrn>
                      <taxonrv>Chondrostei</taxonrv>
                      <taxoncl>
                        <taxonrn>Order</taxonrn>
                        <taxonrv>Acipenseriformes</taxonrv>
                        <taxoncl>
                          <taxonrn>Suborder</taxonrn>
                          <taxonrv>Acipenseroidei</taxonrv>
                          <taxoncl>
                            <taxonrn>Family</taxonrn>
                            <taxonrv>Acipenseridae</taxonrv>
                            <taxoncl>
                              <taxonrn>Subfamily</taxonrn>
                              <taxonrv>Scaphirhynchinae</taxonrv>
                              <taxoncl>
                                <taxonrn>Genus</taxonrn>
                                <taxonrv>Scaphirhynchus</taxonrv>
                                <taxoncl>
                                  <taxonrn>Species</taxonrn>
                                  <taxonrv>Scaphirhynchus albus</taxonrv>
                                  <common>pallid sturgeon</common>
                                </taxoncl>
                              </taxoncl>
                            </taxoncl>
                          </taxoncl>
                        </taxoncl>
                      </taxoncl>
                    </taxoncl>
                  </taxoncl>
                </taxoncl>
              </taxoncl>
            </taxoncl>
          </taxoncl>
        </taxoncl>
      </taxoncl>
    </taxonomy>
    <tool>
      <tooldesc>ESRI 2011. ArcGIS Desktop: Release 10.5 Redlands, CA: Environmental Systems Research Institute</tooldesc>
      <toolacc>
        <toolinst>Proprietary software, must be purchased</toolinst>
      </toolacc>
    </tool>
  </idinfo>
  <dataqual>
    <attracc>
      <attraccr>Instruments were calibrated in the lab using deionized (DI) water to 0 ppb and 10 ppb standards, followed by testing with 1 ppb and 30 ppb standards. No efforts were made to calibrate or evaluate the performance of the turbidity or temperature sensors in the Turner C3 submersible fluorometers.</attraccr>
    </attracc>
    <logic>All values fell within expected ranges, data were checked for transcription errors, omissions and duplicates.</logic>
    <complete>Data set is considered complete for the information presented, as described in the abstract. Users are advised to read the rest of the metadata record carefully for additional details.</complete>
    <posacc>
      <horizpa>
        <horizpar>A formal accuracy assessment of the horizontal positional information in the data set has not been conducted.</horizpar>
      </horizpa>
      <vertacc>
        <vertaccr>A formal accuracy assessment of the vertical positional information in the data set has either not been conducted, or is not applicable.</vertaccr>
      </vertacc>
    </posacc>
    <lineage>
      <procstep>
        <procdesc>Fluorometers were calibrated in the laboratory prior to the experiment using DI water and 0 ppb and 10 ppb standards, followed by testing with 1 ppb and 30 ppb standards.  Following CERC SOP “Methods for Laboratory Calibration of Turner C3 Fluorometer For Riverine Dye-Trace Studies (internal document not publicly available)</procdesc>
        <procdate>20170614</procdate>
      </procstep>
      <procstep>
        <procdesc>Fluorometers were deployed one to two days prior to dye injection at four measurement stations over a 69-km study reach. The distance from the injection location was measured along the approximate thalweg, digitized on 2013 NAIP imagery. Fluorometers were placed approximately four to eight meters from the shore at depths 0.25 to 0.5 meters below the water surface, in areas accessible by wading.</procdesc>
        <procdate>20170628</procdate>
      </procstep>
      <procstep>
        <procdesc>Dye injection occurred on June 29, 2017 at 11:51 MDT. Sixty-one liters of 20-percent solution RWT, diluted by approximately half, were injected using a pump system from tubing positioned approximately 0.3 m below the water surface.  Dye injection occurred along a transect oriented approximately perpendicular to flow and spanned the entirety of the channel from bank to bank at RM 88.6.  The injection was completed within one minute of initiation.</procdesc>
        <procdate>20170629</procdate>
      </procstep>
      <procstep>
        <procdesc>Concentrations of RWT dye, turbidity, and temperature were measured every minute at four sampling stations, located 20.3–68.9 km downstream from the injection location.</procdesc>
        <procdate>20170630</procdate>
      </procstep>
      <procstep>
        <procdesc>Fluorometers were retrieved from deployment locations after the dye plume had passed and fluorescence returned to background levels. Data were downloaded to a field laptop through an RS-232 serial connection.</procdesc>
        <procdate>20170630</procdate>
      </procstep>
      <procstep>
        <procdesc>Data were filtered to remove outliers in measured RWT concentration. All values fall within expected ranges.</procdesc>
        <procdate>20170717</procdate>
      </procstep>
      <procstep>
        <procdesc>Thalweg distance was determined by merging Dawson and Richland counties, Montanna from NAIP ortho imagery (https://gdg.sc.egov.usda.gov/), digitizing the thawleg onto the images, and measuring the respective river miles along the thalweg.  Processing was done utilizing ArcGIS Desktop (ESRI 2011: Release 10.5. Redlands, CA: Environmental Systems Research Institute).</procdesc>
        <procdate>2017</procdate>
      </procstep>
      <method>
        <methtype>Field</methtype>
        <methdesc>Data were collected in June 2017 as part of a dye-trace experiment in the Yellowstone River from approximately Glendive, Montana to Sidney, Montana. Fluorometers were deployed at four measurement stations over a 69-km study reach. Approximately 61 L of Rhodamine WT (RWT) dye was injected on 29 June 2017 at 11:51 MDT. The injection occured along a transect oriented approximately perpendicular to the flow at river mile (RM) 88.6. Injection was performed with a pump system from tubing position approximately 0.30 m below the water surface and was complete within one minute of initiation. RWT dye was diluted by half to facilitate mixing. Fluorometers were placed approximately 4 to 8 m from shore at depths 0.25 to 0.5 m below the water surface, in areas accessible by wading.</methdesc>
      </method>
    </lineage>
  </dataqual>
  <eainfo>
    <detailed>
      <enttyp>
        <enttypl>YSR_DyeTraceExperiment</enttypl>
        <enttypd>Text file containing attributes regarding time, turbidity, temperature and RWT dye concentrations downstream from dye injection location</enttypd>
        <enttypds>Producer defined</enttypds>
      </enttyp>
      <attr>
        <attrlabl>StationID</attrlabl>
        <attrdef>An numeric identifer for the fluorometer sampling station</attrdef>
        <attrdefs>Producer defined</attrdefs>
        <attrdomv>
          <edom>
            <edomv>1</edomv>
            <edomvd>The first sampling station approximately 20277.68 meters downstream from the point of dye injection</edomvd>
            <edomvds>Producer defined</edomvds>
          </edom>
        </attrdomv>
        <attrdomv>
          <edom>
            <edomv>2</edomv>
            <edomvd>The second sampling station approximately 35727.35 meters downstream from the point of dye injection</edomvd>
            <edomvds>Producer defined</edomvds>
          </edom>
        </attrdomv>
        <attrdomv>
          <edom>
            <edomv>3</edomv>
            <edomvd>The third sampling station approximately 53591.02 meters downstream from the point of dye injection</edomvd>
            <edomvds>Producer defined</edomvds>
          </edom>
        </attrdomv>
        <attrdomv>
          <edom>
            <edomv>4</edomv>
            <edomvd>The fourth sampling station approximately 68879.75 meters downstream from the point of dye injection</edomvd>
            <edomvds>Producer defined</edomvds>
          </edom>
        </attrdomv>
      </attr>
      <attr>
        <attrlabl>Northing</attrlabl>
        <attrdef>The northward-measured distance (or the y-coordinate) as measured along approximate thalweg in Universal Transverse Mercator zone 13N,  WGS 84 datum</attrdef>
        <attrdefs>Producer defined</attrdefs>
        <attrdomv>
          <rdom>
            <rdommin>5222800.980</rdommin>
            <rdommax>5263974.434</rdommax>
            <attrunit>meters</attrunit>
          </rdom>
        </attrdomv>
      </attr>
      <attr>
        <attrlabl>Easting</attrlabl>
        <attrdef>The eastward-measured distance (or the x-coordinate) as measured along approximate thalweg in Universal Transverse Mercator zone 13N,  WGS 84 datum</attrdef>
        <attrdefs>Producer defined</attrdefs>
        <attrdomv>
          <rdom>
            <rdommin>525827.889</rdommin>
            <rdommax>555338.781</rdommax>
            <attrunit>meters</attrunit>
          </rdom>
        </attrdomv>
      </attr>
      <attr>
        <attrlabl>disMeters</attrlabl>
        <attrdef>Distance from injection location as measured along approximate thalweg.</attrdef>
        <attrdefs>Producer defined</attrdefs>
        <attrdomv>
          <rdom>
            <rdommin>20277.68</rdommin>
            <rdommax>68879.75</rdommax>
            <attrunit>meters</attrunit>
          </rdom>
        </attrdomv>
      </attr>
      <attr>
        <attrlabl>Date</attrlabl>
        <attrdef>A representation of time in which the smallest unit of measure is a day. The value is expressed in YYYYMMDD.  It represents the date upon which samples were collected.</attrdef>
        <attrdefs>Producer defined</attrdefs>
        <attrdomv>
          <rdom>
            <rdommin>20170629</rdommin>
            <rdommax>20170630</rdommax>
            <attrunit>Date</attrunit>
          </rdom>
        </attrdomv>
      </attr>
      <attr>
        <attrlabl>Time</attrlabl>
        <attrdef>Time of day when sample was collected expressed in 24 hour clock.  Mountain daylight savings time.</attrdef>
        <attrdefs>Producer Defined</attrdefs>
        <attrdomv>
          <rdom>
            <rdommin>0:00</rdommin>
            <rdommax>23:59</rdommax>
            <attrunit>Hours:Minutes</attrunit>
          </rdom>
        </attrdomv>
      </attr>
      <attr>
        <attrlabl>HoursPI</attrlabl>
        <attrdef>The number of 60 minute hours that have elapsed since the dye was injected</attrdef>
        <attrdefs>Producer defined</attrdefs>
        <attrdomv>
          <rdom>
            <rdommin>0.0036</rdommin>
            <rdommax>19.9897</rdommax>
            <attrunit>decimal hours</attrunit>
          </rdom>
        </attrdomv>
      </attr>
      <attr>
        <attrlabl>Rhodamine</attrlabl>
        <attrdef>Rhodamine WT concentration</attrdef>
        <attrdefs>Producer defined</attrdefs>
        <attrdomv>
          <rdom>
            <rdommin>0.92</rdommin>
            <rdommax>3.33</rdommax>
            <attrunit>Parts per billion</attrunit>
          </rdom>
        </attrdomv>
      </attr>
      <attr>
        <attrlabl>Turbidity</attrlabl>
        <attrdef>Measure of the optic property that causes light to be scattered and absorbed rather than transmitted, reported as relative fluorescence units.</attrdef>
        <attrdefs>Producer defined</attrdefs>
        <attrdomv>
          <rdom>
            <rdommin>646.36</rdommin>
            <rdommax>2588</rdommax>
            <attrunit>Relative fluorescence units</attrunit>
          </rdom>
        </attrdomv>
      </attr>
      <attr>
        <attrlabl>Temperature</attrlabl>
        <attrdef>The degree or intensity of heat or cold of the river water at the sampling station, expressed in degrees Celsius</attrdef>
        <attrdefs>Producer defined</attrdefs>
        <attrdomv>
          <rdom>
            <rdommin>18.87</rdommin>
            <rdommax>20.78</rdommax>
            <attrunit>Degree Celsius</attrunit>
          </rdom>
        </attrdomv>
      </attr>
    </detailed>
    <overview>
      <eaover>The entity and attribute information provided here describes the tabular data associated with the data set. Please review the detailed descriptions that are provided (the individual attribute descriptions) for information on the values that appear as fields/table entries of the data set.</eaover>
      <eadetcit>The entity and attribute information was generated by the individual and/or agency identified as the originator of the data set. Please review the rest of the metadata record for additional details and information.</eadetcit>
    </overview>
  </eainfo>
  <distinfo>
    <distrib>
      <cntinfo>
        <cntperp>
          <cntper>GS ScienceBase</cntper>
          <cntorg>U.S. Geological Survey</cntorg>
        </cntperp>
        <cntaddr>
          <addrtype>mailing and physical</addrtype>
          <address>Denver Federal Center, Building 810, Mail Stop 302</address>
          <city>Denver</city>
          <state>CO</state>
          <postal>80225</postal>
          <country>USA</country>
        </cntaddr>
        <cntvoice>1-888-275-8747</cntvoice>
        <cntemail>sciencebase@usgs.gov</cntemail>
      </cntinfo>
    </distrib>
    <distliab>Unless otherwise stated, all data, metadata and related materials are considered to satisfy the quality standards relative to the purpose for which the data were collected. Although these data and associated metadata have been reviewed for accuracy and completeness and approved for release by the U.S. Geological Survey (USGS), no warranty expressed or implied is made regarding the display or utility of the data on any other system or for general or scientific purposes, nor shall the act of distribution constitute any such warranty.</distliab>
  </distinfo>
  <metainfo>
    <metd>20201216</metd>
    <metc>
      <cntinfo>
        <cntperp>
          <cntper>CERC Data Manager</cntper>
          <cntorg>U.S. Geological Survey, Columbia Environmental Research Center</cntorg>
        </cntperp>
        <cntaddr>
          <addrtype>mailing and physical</addrtype>
          <address>4200 New Haven Road</address>
          <city>Columbia</city>
          <state>MO</state>
          <postal>65201</postal>
          <country>US</country>
        </cntaddr>
        <cntvoice>573-875-5399</cntvoice>
        <cntemail>gs-mw-cerc_data_manager@usgs.gov</cntemail>
      </cntinfo>
    </metc>
    <metstdn>FGDC Biological Data Profile of the Content Standard for Digital Geospatial Metadata</metstdn>
    <metstdv>FGDC-STD-001.1-1999</metstdv>
  </metainfo>
</metadata>
