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10 <br />MATERIALS AND METHODS <br />Physical Parameters <br />Water temperatures were monitored at Echo Park and the Waiter <br />Walker Wildlife Area with a Ryan 30-day thermograph. Water temperatures <br />at other stations were taken with a pocket thermometer. Turbidities <br />were measured with a Jackson turbidimeter, and water velocities were <br />determined with a Gurley current meter. <br />Collection of Fish <br />Sampling of fish was conducted from April through November. Shelf <br />and floating ice prevented effective sampling during the winter months. <br />The majority of fish were collected with trammel nets varying in <br />length from 26 to 90 m, with an inside bar mesh of 2.5 cm and an outside <br />bar mesh of 25 cm. Suitable areas were sampled using a 30 m bag seine <br />with 2.5 cm mesh. In addition, small fish were captured using a 5 m <br />seine with 3 mm bar mesh. Swift, shallow water areas were sampled with <br />an electroshocker consisting of a 120 volt DC generator with a variable <br />voltage pulsator mounted on a 3.6 m aluminum boat. Electrofishing was <br />relatively ineffective during periods of high water because of swift <br />water-velocity and high turbidity. The efficiency of the trammel nets <br />was also reduced at these times due to large amounts of floating debris <br />and high water velocities. <br />Endangered or threatened fish were returned unharmed to the river, <br />although a few died from injuries suffered during capture. Dead