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the surface) with a Marsh-McBirney current meter. Microhabitat use by adult <br />Colorado squawfish was also evaluated by collecting depth, velocity, and <br />substrate data 1 to 2 m inshore (shallow) and offshore (deeper) from the <br />signal source in 1984 and 1985. Substrate type was obtained by direct <br />observation and by probing with a wading rod. For additional information on <br />radiotelemetry methods see Tyus {1987). <br />LARVAL COLORADO SQUAWFISH COLLECTIONS <br />Systematic basin-wide collections of larval Colorado squawfish were <br />initiated in the Green, Yampa, and White rivers in 1981 to aid in locating <br />potential spawning areas. Qualitative (presence/absence) and quantitative <br />(catch per effort) sampling programs were continued through 1985 in Green <br />River to confirm existence of suspected spawning sites and to establish <br />spawning dates. Qualitative samples were also taken at weekly intervals <br />during July and August, 1983 to 1985, in "best" backwater habitat encountered <br />at the two confirmed Colorado squawfish spawning areas (Yampa Canyon, Yampa <br />Aiver and Gray Canyon, Green River) in order to obtain presence/absence and <br />growth data for Colorado squawfish. Catch per effort data were collected from <br />shallow backwaters (water depth < 12 in), deep backwaters (water depth > 12 <br />in), and shorelines using a systematic sampling program in 1981, 1964, and <br />1985: <br />1. At the top of each stratum, a team proceeded downstream 8 km (5 mi) <br />and initiated sampling. One shallow and one deep backwater were2 <br />sampled twice (two replicates) with a larval seine (about 0.8 mm <br />mesh) in the first 0.8 km (0.5 mi) reach. If all habitat types were <br />not available in the initial 0.8 km (0.5 mi) reach, those missing <br />were sampled in the remaining 7.2 km (4.5 mi) of the section. <br />Records of depth, velocity, and substrate, as well as sampling <br />effort, were taken for each sample site. Sampling sites within <br />15 <br />