Laserfiche WebLink
<br />26 The State of the Colorado River Ecosystem in Grand Canyon <br /> <br />studies reported above, howevCl~ have demonstrated that <br />in the postdam Colorado River the relationship between <br />110w and sand transport is not stable but instead shifts <br />quickly and substantially relative to the grain size of sand <br />on the bed of the river (which is controlled by tributary <br />inputs and mainstem 110ws). Rubin and Topping (200 I) <br />and Rubin and others (2002) showed that the grain size <br />of the sand in the regulated Colorado River ecosystem <br />depends greatly on the recent histOlY of tributary activ- <br />ity. For example, during low tributary 110w periods the <br />only source of sand to the mainstem Colorado River <br />is that on the channel bed and in eddies, and that sand <br />tends to be much coarser than tributary-delivered sand <br />because of the winnowing of the finer sizes. \Vhen <br />tributaries are 1100ding and delivering large quantities of <br />fine sand (fig. 8), however, the supply is no longer lim- <br />ited to the coarser channel bed sand, resulting in much <br />higher mainstem sand concentrations and, hence, greatly <br />increased suspended-sediment export for any given 110w <br />released from the dam. <br /> <br /> <br />Figure 8. Looking upstream into Glen Canyon from the <br />Paria River confluence with the main channel Colorado River <br />during a Paria River flood. Tributary inputs of sand, such as <br />the one pictured, now encounter clear Colorado River water <br />because Lake Powell traps incoming fine sediment The <br />Paria River is the primary source of sand to Marble Canyon <br />but is only about 6% of the predam sand supply (photograph <br />by Scott A. Wright, U.S. Geological Survey). <br /> <br />Because sand transport cannot be predicted based <br />on discharge alone, sediment budgets for the Colorado <br />River in Grand Canyon can only be constructed based <br />on measurements of sand transport at a frequency great <br />enough to capture changes in concentration and grain <br />size resulting from tributary inputs. Fundamentally, <br />the conclusions drawn by the EIS team, which are not <br />supported by the more recent data, resulted from a lack <br />of continuous data in the postdam era; that is, if daily <br />records had been continued beyond 1972 and into the <br />EIS period, then the fine-sediment budget would have <br />been constructed based on these data rather than on <br />stable rating curves. Recent sediment budgets suggest <br />that under this scenario the conclusions of the EIS would <br />have been different and possibly would have led to a <br />different strates')' for operation of Glen Canyon Dam in <br />1996. Though it is somewhat costly to collect long-term, <br />high-frequency sediment-transport records, in this case it <br />may have prevented 13 yr of dam operations that have <br />continued to erode sandbars from Grand Canyon. <br /> <br />Current Experimental <br />Plan for Fi ne Sedi ment <br /> <br />Because recent research has shown that sand does <br />not accumulate on the river bed in Marble and Grand <br />Canyons under normal Record of Decision dam opera- <br />tions, scientists have recently proposed two possible field <br />tests of dam operating options that might more effec- <br />tively conserve limited, downstream sand resources. One <br />approach is to implement floods immediately following <br />large tributary inputs that commonly occur in late sum- <br />mer and early fall. A second approach is to follow tribu- <br />tary sand-input events with low flows, in order to limit <br />export and retain most of the sand input, until flooding <br />can be implemented. This approach would require a <br />change in the pattern of monthly release volumes and <br />associated dam operations because July and August <br />releases of recent drought years still resulted in half of <br />the sand introduced by a tributary flood being exported <br />within days or weeks (Rubin and others, 2002). <br />In September 2002, the U.S. Department of the <br />Interior (2002) approved implementation of the second <br />approach described above. Under this plan, changes <br />in dam operations and restoration floods are linked to <br />triggering thresholds based on sand inputs [rom the Paria <br />River and lesser Marble Canyon tributaries and retention <br />o[ sand in Marble and Grand Canyons. For example, <br />the "autumn sediment input" scenario described in the <br />2002 environmental assessment (EA) (U.S. Department of <br />