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Last modified
7/14/2009 5:02:30 PM
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5/20/2009 5:14:13 PM
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UCREFRP
UCREFRP Catalog Number
7393
Author
Harrington, W.
Title
Endangered Species Protection and Water Resource Development.
USFW Year
1980.
USFW - Doc Type
LA-8278-MS,
Copyright Material
NO
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<br />often difficult to confirm (even experts can have trouble distinguishing sand- <br />hills and whoopers from a distance). The recently established Cooperative <br />Whooping Crane Tracking Project, an attempt to gather.data in a more systematic <br />fashion, may remedy these shortcomings. However, 3 years of probable and con- <br />firmed sightings (1976-78) seem to support the earlier data, with 20% of all <br />sightings in Nebraska (Table IIIc). This project cannot determine the behavior <br />of individuals, and so much remains to be learned about whooper migration pat- <br />terns. Next year, the cranes will be fitted with telemetric devices, and many <br />gaps in the current picture will be filled in. <br />6. An indequate supply of roosting sites in the Central Flyway will <br />reduce the spec ies chances of survivaL Not knowing how the whooping crane <br />will respond to changes in its migratory habitat makes it difficult to estnnate <br />the effects of such changes on the crane's mortality. It is nontheless in- <br />structive to look at the existing data on crane population. In 1938, when <br />Aransas National Wildlife Refuge was established, the Aransas flock numbered <br />only 18 individuals. By 1976 it had grown to 69 birds (see Fig. 1). In other <br />words, the population of the Aransas Flock nearly quadrupled during precisely <br />, the period when the channel width in the critical habitat along the Platte <br /> <br />, <br />decreased by 50%. These data suggest that the loss of habitat along the <br />crane's migration route was not a limiting factor. .C. i <br />"A It is not completely understood why the whooper population has improved <br />V"~~~;0V~0 dramatically, although when average hatching and death rates by decade are <br />~\l'1'~)v\ computed, some suggestive trends emerge (see the note to Table IV for defini- <br />\ \:l"~ tions of hatching and death rates). As shown in Table IV, the death rate for <br />vfJ',' the Aransas population declined from 0.169 in the decade 1938-47 to 0.065 in <br />the interval 1968-75. This decline must be the principal reason for the dram- <br />atic population increase over this period and to some extent is the result of <br />the additional protection provided against hunters by the Aransas sanctuary. <br />But though the wildlife refuge opened in 1938, the population in 1955 was the <br />same as in 1940. Except for brief periods in the early 1960s and early 1970s, <br />the population increase since 1954 has been fairly steady. Over the same <br />period, however, the birth rate also declined considerably--from 0.206 to <br />0.111. Why this should have happened has puzzled biologists at the Fish and <br />wildlife Service. <br /> <br /> <br />42 <br />
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