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Flight Procedures <br />Fixed-wing aircrafts were flown between 300-350 feet at 90-100 mph. <br />• Helicopters were flown at an altitude of 150-200 feet and an air speed <br />of 60-70 mph. A mapper/navigator accompanied the spotter whenever pos- <br />sible. The same pilot consistently flew each route in order to minimize <br />between-flight differences. A11 routes were flown between 8:00 - <br />12:00 a.m., weather permitting. The San Miguel and Gunnison Rivers <br />were also flown at dusk (1-1~ hours before dark) to determine night <br />concentration areas. The San Miguel River was flown the morning <br />following the first of these evening flights to determine the fluctu- <br />ation in eagle use between these periods. <br />During each flight the following information was recorded: temperature, <br />Kind speed, average aircraft altitude and speed, and starting/landing <br />times. When an eagle was sighted, age class, location, activity and <br />time were recorded. Each sighting was assigned a number, plotted on a <br />map, and the information collected was transcribed onto data forms (see <br />Figure 1). A tally of eagle numbers and flight times were recorded on <br />aerial survey data sheets (see Figure 2). <br />Ground Procedures <br />rround surveys were conducted subsequent to aerial surveys in those <br />areas accessible by roads. Survey routes, weather conditions, waterway <br />condition, eagle numbers, locations and activities were recorded on <br />ground summary data forms (see Figure 3). <br />• Consistently used perch trees and night roosts were checked periodi- <br />cally for prey remains and castings. These were collected in plastic <br />bags and labeled with dates and locations for future analyses. <br />Attempts were made at the Disappointment Roost to observe the behavior <br />of the birds during the day and also record the direction these birds <br />flew when departing from the roost each morning in order to determine <br />hunting areas: Behavioral activities and times were recorded on obser- <br />vation data sheets (Figure 4). <br />Efforts were made to estimate rabbit population numbers in high and no <br />eagle use areas in order to determine if rabbit species are a sig- <br />nificant component of the prey base. A 15-mile transect and 12.5-mile <br />transect were driven along roads in Disappointment and Dry Creek Valleys <br />which were high use areas. A 15-20 mile transect was driven through <br />Paradox Valley, which received little or no use by eagles. Open bed <br />trucks were driven at 10 mph while a biologist spotlighted areas on <br />either side of the road using an IPF-802 Halogen quartz light. Species <br />of rabbit, number of rabbits, mileage and perpendicular distance from <br />the rabbit to the truck were recorded. Each of these transects was re- <br />peated on three consecutive nights. Results were tallied and numbers <br />averaged. <br />r~ <br />