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5 <br />STUDY AREA <br />Field activities were conducted in the Colorado (Mesa County) and Yampa <br />Rivers (Moffat County) (Figure 1). The Colorado River study area includes <br />an approximately 32 km (20 mi) river reach from the vicinity of Loma <br />to the Colorado-Utah state line. The Yampa River study area includes <br />an approximately 95 km (59 mi) reach from the upper end of Cross Mountain <br />r Canyon to the confluence with the Green River. Approximately 75 km <br />(46.5 mi) of the study area are within Dinosaur National Monument. <br />METHODS <br />General. Field sampling was conducted during periods which reflected <br />pre-runoff, peak-runoff, and post-runoff conditions in the Colorado and <br />Yampa study areas. Collections were made during 4-5 day field trips <br />utilizing a power boat and inflatable rafts in the Colorado while rafts <br />and canoes were used in the Yampa. Cross Mountain Canyon was surveyed <br />entirely on foot since the extremely turbulent nature of the canyon <br />made float trips unsafe. Fishes were collected with 3.0 x 1.2 m and <br />1.0 x 1.2 m seines (1.6 mm square mesh) and dip nets (0.79 mm square <br />mesh). Samples were collected according to the "qualitative representative <br />sample" approach (Hocutt et al., 1974) i.e., all available habitats <br />that could be seined were sampled to obtain a representative collection <br />of species at a given locality and which would provide relative abundance <br />information, recognizing the bias of the collection technique employed. <br />Current velocity was measured with Marsh-McBirney or Pygmy-Gurley flow <br />meters, or float techniques. Water temperature was measured with a Taylor <br />thermometer. <br />In order to correlate fish distribution and relative abundance with the <br />wide range of measurable variables, samples were collected according to <br />a detailed habitat stratification approach which was designed to reflect <br />the geomorphic, hydrological, and ecological variables of the drainages <br />(Appendix A). This approach incorporated methods outlined by Herrington <br />and Dunham (_1967) and Platts (1974), but was modified to reflect conditions <br />of larger streams. In order to interface data with both those collected <br />by DOW personnel in the NW Region and the U.S.F.W.S., habitat designations <br />were coded to be computer compatible with the FWS MANAGE program and data <br />are currently being entered at the Colorado State University Computer <br />Center, Fort Collins. Standardized field/laboratory data forms are employed. <br />Within each study area, three types of sample sites were designated. <br />"Intensive" sections were randomly selected prior to each field trip <br />utilizing a table of random numbers. This process required the initial <br />random selection of one location within the study area, corresponding <br />with a designated river mile. This site, plus each river mile every <br />_ 5 miles (8 km) above and below the random site were designated as intensive <br />sampling sites. At each intensive site, all recognizable habitats- were <br />sampled for a distance of 0.25 (0.4 km) miles above and below the mid-point. <br />Typically, depending upon the initial random site selection, 9-10 intensive <br />sites were designated for the Yampa River study area and 5-6 sites for the <br />Colorado River study area. "Intervening" sections were localities which <br />