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Whooping Crane Migrational Habitat Use Draft (2)
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Whooping Crane Migrational Habitat Use Draft (2)
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Last modified
1/26/2010 4:37:13 PM
Creation date
6/3/2009 9:41:23 AM
Metadata
Fields
Template:
Water Supply Protection
File Number
8461.100
Description
Adaptive Management Workgroup
State
CO
Basin
South Platte
Water Division
1
Date
8/6/2008
Author
Shay Howlin, Clayton Derby, Dale Strickland, Western Ecosystems Technology, Inc.
Title
Whooping Crane Migrational Habitat Use Draft
Water Supply Pro - Doc Type
Report/Study
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Aerial Survey Detection Rates <br />Experimental trials were conducted to compare detection rates for the many factors relating to <br />the implementation of the protocol. Detection trials were conducted using a stratified random <br />survey design. Single whooping crane decoys (sandhill crane decoys painted to resemble <br />whooping crane plumage) were randomly placed on accessible conservation lands in the study <br />area in either the channel stratum (river) or upland (return) stratum and their location was either <br />recorded or not recorded during the aerial survey (PRESP 2005). The resulting strata estimates of <br />detection probability are applicable to the types of aerial transects surveyed. Detection trials were <br />conducted in the study area during each of the 11 survey seasons. All trials were conducted using <br />single decoys randomly placed on accessible conservation lands. A total of 176 decoy trials were <br />deployed during the Cooperative Agreement period for detection by the systematic flights: 111 <br />decoy trials were conducted in the river in the wetted channel and 65 decoy trials were conducted <br />within the entire study area in the return strata (Table 1). Flight orientation covariate information <br />was available for 168 of the decoys. <br />A predictive model of detection probability was developed and used to calculate actual sample <br />inctusion probabilities for monitoring flights. Models were parameterized assuming the number <br />of decoys detected during the aerial flights followed a binomial distribution with parameters n <br />(the number of decoy trials) and p(the detection probability). A list of candidate models was <br />generated through listing all possible combinations of the predictor variables: contractor, year, <br />season, flight direction, flight height, flight orientation, and survey strata. Models were fit using <br />logistic regression and the Akaike information criterion (AIC) was calculated to select the most <br />likely model given the data. <br />Movement Pattern Summary <br />The average distance a crane group moved was estimated by averaging each successive known <br />movement, where movement was defined as the straight line distance between two consecutive <br />locations. Crane groups were considered to have moved if the crane group flew to a new location <br />or the crane group walked to a different land cover type. Distances were averaged across all <br />movements observed for a crane group. The average distance moved was estimated across the 13 <br />crane groups with multiple observations, using the crane group designation made by the <br />USFWS. Movements were mapped on color infra-red photographs taken during fall 2003, with <br />the length of time a crane group spent in an area indicated by the size of the mapped syrnbol and <br />arrows to indicate the direction of movement. <br />The average distance moved was used to define the area within which a crane group will make a <br />"local area" selection of habitat within the study area. While there are other ways to define the <br />local area, WEST chose this definition because it could be calculated with the available data and <br />it adequately represents the average distance a crane group flies when intending to continue use <br />of the study area. It is assumed the distances recorded by the ground crews were a random <br />sample of distances moved by crane groups using the study area.
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