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<br />rivers. Whi I e less sediment load Is beneficial to maintaining substrate <br />conditions for viable spawning, an adequate sediment supply must be <br />maintained for beach replenishment and riparian vegetation In the canyon. <br />Important to the canyon ecology is the relationship of endemic phreatophytes <br />(wiI lows and cottonwoods) and their confrontation with invading tamarisks <br />over available sandy beaches for seed germination. The cottonwoods in the <br />riparian zone require moist, sandy substrate during seed deposition and high <br />flows to scour years i ng growth of tamarisks. The substrate must be <br />relatively free of al ten vegetation for cottonwood seed germination and <br />growth. Further, the beaches are important to the aesthetic and <br />recreational resource values In the canyon. The interaction of all the <br />biological and physical processes occurring in the canyon require thorough <br />understanding before peak flows and annual water volumes are reduced in the <br />upstream tributary systems. <br />The effect of reducing the discharge In the Little Snake w i l l be to <br />reduce the sediment load to the canyon. Concomitantly, reducing the water <br />supply In the Yampa River upstream of the confluence with the Little Snake <br />River will have the effect of limiting the river's abil ity to transport the <br />sediment load In the canyon. The possible options for water development <br />must be evaluated in terms of quantifying how the equi l ibr i um of the <br />hydrologic system is disrupted. <br />To Initiate the project, the daily flow discharge and sediment load <br />data base was reviewed, this included reviewing data from the reports by the <br />NPS (O'Brien, 1982 FI ug, O'Brien, et al., 1983 O'Brien, 1984) and the USGS <br />(El I lott, et al . , 1984), and reviewing the USGS gaging station data In <br />computer fit es. It was discovered during this review that there were <br />missing data In the USG S da i I y f I ow records, that the most recent years <br />(exceedI ngly wet years) had not yet been processed i nto the f II es, and that <br />the sediment dl sch arge rel ati onsh i ps req ui red f urther evai uati on. The <br />fol I ow i ng tasks were performed to remedy these probl ems. <br />1 . Seventy-two random bl ocks of el ght day, da i I y L i ttl a Snake w ater <br />discharges were missing from the computer data base. Most of <br />missing data were extracted from the pub) fished USGS water supply <br />records in the library and added to computer files. Several blocks <br />of missing data from the period 1928 to 1934 had to be obtained <br />from the Colorado State records as the USGS relinquished <br />responsibility for taking the Little Snake discharge measurements <br />during this period. <br />2. The water years of 1983 and 1984 were added to the computer f i I es <br />completing the current published USGS database (64 years dating <br />from 1921). These years constitute very high vol ume water years <br />with 1983 the highest volume water year on record. <br />3. Al I three databases (USGS gaging station USGS, El I iott data and <br />the NPS O'Brien data) had water-sediment discharge regressed <br />relationships based log-log data transformation using a <br />mathematical I east squares best f it to the data. This regression <br />method underestimates predicted sediment I oads and the <br />4