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Crane Workshop, China) that describes habitat use. Once again, wetlands were the <br />predominant habitat type for roosting. Also, refer to Amy Reichert's 1999 Ph.D <br />dissertation on whooping crane habitat use from the University of Nebraska. <br />Development of wetlands in the Platte Valley by The Nature Conservancy and <br />other conservation groups has resulted in use by whooping cranes as well. Even at <br />Bosque Del Apache NWR in New Mexico, the cross - fostered whoopers roost in the <br />highly regulated water impoundments adjacent to the Rio Grande River unless the <br />impoundments freeze. Only then will they roost in the river. <br />My point is that off -river roost sites must be included not only for biological but <br />also for economic reasons as well. NPPD's Cottonwood Ranch is a case in point. As <br />you know, the FWS intends to clearcut a gallery forest and engineer a channel which <br />meets the definition of roost habitat. The purple loosestrife problem, the sediment <br />concerns, and the ongoing disking necessary to maintain the open river channel will be a <br />costly experiment. This does not even consider the loss of biological diversity resulting <br />-from the clearcutting efforts currently underway. It may be less costly and more <br />beneficial to whoopers to create wetlands in the former wet meadows there. By restoring <br />marginal croplands to prairie and wetlands, the same enefits to whoopers may be <br />attained. If not, the more intensive clearcutting route can be taken. <br />It is interesting to note that since the completion of the Kingsley Dam in 1941, the <br />whooping crane population has increased 13 -fold. My point here is that use or <br />population size may not necessarily prove a cause and effect relationship. I wonder if the <br />Platte River would even be considered if the FWS was charged with designating critical <br />habitat today. Whooping crane experts that I have visited with would be hard pressed to <br />consider the Platte River given our current state of knowledge. Certainly none would be <br />willing to state on a witness stand that the continued existence of the species would be in <br />jeopardy if the Platte River were to disappear. That aside, the development of off -river <br />roost sites will not diminish the need to maintain instream flows due to the direct positive <br />relationship of river stage to groundwater levels in the adjacent aquifer. <br />On page 4 of the Draft R3 -1 Document states "In February and March, rising <br />ground water levels thaw the soil and initiate biological responses of soil organisms." <br />What specific studies on what soil organisms were used as a basis for this statement? I <br />am not aware of such studies yet I know this argument has been used as a basis for <br />instream flow requests and other legal proceedings. If there are any, you should include <br />them in this document with supporting evidence. <br />Least Terns and Piping Plovers <br />At the February Monitoring and Research Workshop held at the Trust offices, it <br />was interesting to note that the species experts did not think it wise to create permanent <br />-y nesting habitat due to the problems associated with predation. That the central Platte <br />River does not offer any naturally occurring nesting habitat for these species is amply <br />demonstrated by fact that there were no tern or plover chicks were known to fledge on <br />any natural river sandbar during the entire decade of the 1990's. A 50 -60 day window of <br />flows less than about 1500 cfs during late May through mid July is necessary to allow for <br />nesting and subsequent fledging. This did not happen in the 1990s. Nests and /or young <br />`' were flooded out. The efforts exhibited by conservation groups to provide nesting habitat <br />