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Aspinall Unit did not adversely affect the endangered fishes in the Gunnison <br />River because their numbers had already been reduced by a variety of factors-- <br />particularly the blockage of movement into the Gunnison River by the Redlands <br />Diversion Dam. However, there is a remnant population of Colorado squawfish <br />in the Gunnison River above the Redlands Dam. It is not known whether the <br />fish moved above the diversion dam during the relatively short periods (due to <br />dam maintenance or other activities) when upstream movement is possible or <br />whether they were spawned above the diversion. If spawning is being attempted <br />in the Gunnison River, the reduced temperatures (even though the reduction is <br />small) would decrease the probability that it would be successful. Further, <br />the reduced temperature would decrease the probability of success if future <br />reintroduction efforts are directed at the Gunnison River. <br />Colorado River temperatures are essentially unchanged by the Aspinall <br />Unit. Therefore, water temperature changes as a result of the Aspinall Unit <br />probably did-not affect the endangered fishes in the mainstem Colorado River. <br />Sediment Load <br />It is unknown how the reduced sediment load has affected the endangered <br />fishes. Reduced sediments have affected the Gunnison River (e.g. the armored <br />bottom in many areas [Sanford and Ward 1983]), but because the fish were <br />already greatly reduced before Aspinall was completed, it is unlikely that the <br />sediment changes caused their decline. However, the changed substrate may <br />affect the success of future reintroductions. <br />The primary effect of reduced sediment levels involves the maintenance <br />of backwaters in the lower Colorado River, an important habitat for young-of- <br />the-year Colorado squawfish. However, the sediment load of the Colorado River <br />23 <br />