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<br /> <br />18 <br /> <br />Gila species. <br />often receive <br />periods. <br /> <br />If placed in moderate current, however, the fish would <br />much external abrasion if left in the trap for long <br /> <br />Physical Measurements <br /> <br />An assemblage of compact, durable, time efficient equipment was <br />procured to collect physical and chemical data to permit the compilation <br />of as much data as possible with the highest possible level of accuracy. <br /> <br />Probably the most time-saving device utilized relative to traditiona' <br />equipment and methods was the Marsh-McBirney Model 201 portable water <br />velocity meter. This was a direct-reading device which reduced the <br />time of taking water velocity measurements by 70-80% from the older <br />methods of counting the rotations of a water wheel. Velocity measurement, <br />were taken at 0.6 the distance from the surface (Bovee and Milhous <br />1978). Distances between shorelines were measured using a hand-held <br />range finder and depths were recorded with a collapsible stadia rod <br />and a Lowrance Model LRG l5l0A depth finder. The Lowrance depth- <br />finder has a strip chart which provides an opportunity to enter notations <br />relative to station location and descriptive notes pertaining to <br />important features on the printout. <br /> <br />Total dissolved solids, salinities and conductivities were measured <br />with a Yellow Springs Model 33 meter which has a combined conductivity <br />and temperature probe. Conductivity is expressed as micromhos per <br />centimeter. Salinity is temperature compensated and recorded in grams <br />per kilogram. A Hach Model DRIl colorimeter was used to measure pH, <br />dissolved oxygen and turbidity. Turbidites were measured in forazin <br />turbity units (FTU) which are equivalent to Jackson turbidity units. <br /> <br />Fish weights were taken with Chatillon 2g x 1000 g or 20 g x 5 kg <br />platform scales. <br /> <br />Fish Collection Gears <br /> <br />As pointed out earlier, rivers present a variety of fluvial <br />conditions that require unique sampling methods. Some areas such as <br />the swift, deep canyons present an almost insurmountable obstacle to <br />procuring representative fish samples with current technology. <br /> <br />There was no single technique which efficiently salnpled all <br />habitats for all sizes of fish. We strived to use the gear or combinati( <br />of gears that would provide a good, cross-section of the fish population <br />in each habitat. Table 3 presents the general habitat types within <br />the primary gear types employed. <br /> <br />The gear probably utilized to the greatest extent were seines. <br />While a variety of seine sizes and meshes were used, the two utilized <br />most were 15 x 4 ft, 1/8 in mesh and 30x 6 ft, 1/4 in mesh nets. <br />