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largely inundated suitable sandbar habitat at the <br />and piping plover. Extended no flow periods oc( <br />Figure 7). The historical tendency of the central <br />is well documented, was not conducive to succf <br />would have reduced, and likely eliminated, adjac <br />Finally, despite regular observations of least tern <br />the century, historical sighting records provide n <br />the Platte River from east of the confluence of the <br />The first record of least tern nesting along the cE <br />perennial flows were established in this reach by <br />plovers in the same area was in 1950. <br />These considerations indicate that regular use of <br />and including the Big Bend reach, by least terr <br />occasioned by the onset of permanent, moder; <br />operation (EA, 1988) and the availability of e <br />construction of I-80 and subsequent sand and gr <br />habitat (please see piping plover data for Lake Mc <br />Water storage has reduced drastic water level c] <br />acted to limit utilization and/or nesting success t] <br />reduction of adjacent food supplies, and exposure <br />existing piping plovers and least terns, water de <br />conditions which allow them to inhabit the Platte ] <br />Prior to flow regulation, extreme flow vari; <br />substantially diminished, and likely eliminated, <br />Platte River channel upstream of the Loup River. <br />ne of arrival and nest selection for the least tern <br />rred during the nesting season prior to 1941 (see <br />latte to go dry during the summer months, which <br />sful nesting. Prolonged dry riverbed conditions <br />nt feeding areas and exposed nests to predation. <br />and piping plovers in Nebraska since the turn of <br />reference to regular occurrence of species along <br />orth and south Platte to the Loup until after 1941. <br />.tral Platte was in 1942 near Lexington, the year <br />iater project operation. The first report of piping <br />he Platte River upstream of the Loup confluence, <br />and piping flow is a more recent phenomenon <br />e flow conditions resulting from water project <br />tensive habitat provided by sand pits from the <br />vel mining as well as the availability of "shore" <br />;onaughy). <br />nges from floods and droughts that historically <br />ough inundation of potential or active nest sites, <br />f nest sites to predation. Rather than threatening <br />-lopment and land use changes has created the <br />ver upstream of the Loup. <br />ility during the breeding season would have <br />.bitat suitability and reproduction potential in the <br />The habitat far the least tern and piping plover on the central Platte has been enhanced, if not <br />created, as a result of water development activities. The states are now asked to create the near ideal <br />conditions, which may have occurred historically i other areas such as on the Missouri River, but <br />which never existed historically on the Platte Riv r upstream of the Loup. This is an inappropriate <br />use of the powers of the Endangered Species Act. Rather than jeopardizing the species in question, <br />water development activities in the Platte have cre ted the habitat now designated as "critical." <br />4.0 Questions Regarding Procedures to be Usedl by the Committee <br />The Colorado Water Conservation Board has re <br />provided on the NAS website. We have a number <br />be used by the Committee. These questions are in <br />provided below. <br />ewed the scope of work for the Committee as <br />f questions regarding methods and procedures to <br />-rted into the Committee's scope of work and are <br />We believe that addressing these questions is cri i <br />work. As we review the Committee's draft report, <br />basic questions. However, should the Committee <br />directly to the Board, that would be most appreciat i <br />d to successfully completing the Committee's <br />will be looking forward to the answers to these <br />?ose to address these questions with a response <br />A- 18