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<br />A. <br /> <br />en <br />o c:: <br />- 0 <br />Ol - <br />> c:: <br />'';:; 0 <br />CO :.= <br />~E <br />..c::- <br />,-,en <br />",en <br />Olen <br />~ - <br />.!: u-) <br />"'-: <br />'" 0> <br />'" ::l <br />E<( <br />"0 c:: <br />c:: 0 <br />'" - <br />en '" <br />;5 <br /> <br />B. <br /> <br />- <br />'" <br />;5_ <br />B ~ 2.2 <br />g; 9 <br />.~ .~ <br />a;;: 1.1 <br />~..s <br />'-'N <br />"'0 <br />e ~ 0.0 <br />.':: -.. <br />~~ <br />'" ::l <br />E ~-1.1 <br />~ 0 <br />'" <br />en <br /> <br />c. <br /> <br />- <br />'" <br />;5_ <br />o '" 2.2 <br />_ c:: <br />Ol 0 <br />> - <br />'g .2 <br />a;;: 1.1 <br />~E <br />'-'M <br />"'0 <br />010 <br />.~ :.. 0.0 <br />~~ <br />'" ::l <br />E' <br />-g 5 -1.1 <br />'" <br />en <br /> <br />Influence of Glen Canyon Dam Operations on Downstream Sand Resources 25 <br /> <br />6.6 _. _ _ Mass-balance uncertainty envelope <br />5.5 -- Water discharge <br /> <br />4.4, U. <br />3.3 -.. . ~ 1,;,11 ... . _.-. <br />III ... .. ..,.. <br />2.2 t <br />1.1 <br />Accumulation <br />0.0 <br />-1.1 <br /> <br />~~:~~~ en <br />40,000 u <br />35,000 <br />~K~~~ ~ <br />lK~~~ ~ <br />1 0,000 ~ <br />5,00~ .f <br />'" <br />Ol <br />Ol <br />-' <br />Ol <br />;5 <br />- <br />'" <br />Ol <br />~ <br />'" <br />..c:: <br />'-' <br />.~ <br />o <br /> <br />I' _-., Erosion,. r '.. <br />,.....- I ------. I "'- I.......... <br />\,.._1_-...1 ---....... --. <br />-2.2 '. <br />-3.3 '-,..! .....--.........__....:r'.. <br /> <br />-4.4 ..-.....1--........- <br /> <br />.5.5 <br /> <br />~ ~gg g g~~ ~ ~g8 8 ggg g ggg <br />.- .....NN N N~........... .....NN N NNN N NNN <br />g'~.g ~ g Ei.g t; g g.g t; g~.g ~ g~.g t; <br /><X zu..~ <t zu....::2 <C Zu..:2; <t zu..:2: <( zu...~ <br /> <br />3.3 <br /> <br />35,000 <br />30,000 <br />15,000 ~ <br />10,000 ~ <br />15,000 ~ <br />10,000 ~ <br />5,000 >- <br />o :: <br />Ol <br />LL <br />'" <br />Ol <br />Ol <br />-' <br />- <br />'" <br />Ol <br />~ <br />'" <br />..c:: <br />'-' <br />.~ <br />o <br /> <br />... -. Mass-balance uncertainty envelope <br />.- Water discharge <br /> <br /> <br />11M' <br />.a:.ftr4Ml'a;Nl <br /> <br />----, .,t <br />, ' <br />I _.. _ __.. -hcumui'ation-...... _.. <br /> <br />._-. <br /> <br />Erosion <br /> <br />r- <br /> <br />'. <br /> <br />\ <br /> <br />Linle Colorado River flood <br /> <br />-2.2 <br />J\l\~ 1111l\e~.1\)\l\o\o~ .1\)\llJall.lllll'1;\at. 11l1l, 1;\a~ 1\)\l\\l\~ 11l1l, <br /> <br />3.3 <br /> <br />35,000 <br />30,000 <br />15,000 en <br />10,000 ~ <br />15,000 ~ <br />1 0,000 ~ <br />5,000 ~ <br />o O:i <br />LL <br />'" <br />Ol <br />Ol <br />-' <br />- <br />'" <br />Ol <br />~ <br />'" <br />..c:: <br />'-' <br />.~ <br />o <br /> <br />- -. Mass-balance uncertainty envelope <br />- Water discharge <br /> <br />'!URU <br />Mil/Mrm <br /> <br /> <br />ml~~~M\i~ <br /> <br />,______ t <br /> <br />...... - Accumulatio!l <br />.. -. ... Erosion <br />"- <br /> <br />-".----- <br /> <br />"'. <br /> <br />\ <br /> <br />. <br /> <br />Paria River flood <br /> <br />-2.2 <br />J\l~ 101l, se~.l\)\l' \'lo~ .11l1l' Jail. 1IlMN\at.l01l~1;\a~ 11l1l~ J\l\~ 11lM <br /> <br />Figure 7. Mass balance of sand between Lees Ferry and <br />Grand Canyon gages from August 1999 through July 2004 (A) and <br />separately for sediment years (July-June) 2003 (8) and 2004 (C). <br />Mass balance is cJmputed by subtracting measured, mainstem <br />suspended-sand export (10% uncertainty) from estimated and <br />measured sand inputs from the Paria River (20% uncertainty) and <br />Little Colorado Riv'3r (30% uncertainty). as well as from estimated <br />inputs from numerous lesser tributaries (50% uncertainty). The <br />measurements illustrate the rapid export of tributary inputs by high <br />dam releases and the continued overall loss of sand from Grand <br />Canyon under the modified low fluctuating flow (MLFF) alternative, <br />even during the drought-hydrology, minimum-volume release years <br />of 2003 and 2004 (modified and updated from Rubin and others, 2002). <br /> <br />others (1976). Most significantly, the sand mass <br />balance remained negative during water years <br />2000 through 2004, despite 5 consecutive years <br />in which minimal release volumes (8.23 million <br />acre-feet (10,148 million m3)) from Lake Powell <br />occurred during prolonged drought in the upper <br />Colorado River Basin. These measurements <br />and calculations of sand transport also show <br />that tributary inputs are typically transported <br />downstream and out of the canyon within a few <br />months under typical Record of Decision opera- <br />tions (Rubin and others, 2002). <br /> <br />. Repeat topographic mapping of sandbars (Hazel <br />and others, 1999) showed that the 1996 BHBF <br />did increase the surface area of high-elevation <br />sandbars, but more than half of the sand depos- <br />ited at higher elevations was taken from the lower <br />portions of the sandbars (Schmidt, 1999) rather <br />than being derived from tributary sand supplies <br />accumulated on the channel bed, as originally <br />hypothesized in the 1995 EIS. <br /> <br />. Repeated surveys of channel cross-sections (Flynn <br />and Hornewer, 2003) revealed erosion at 55 of the <br />57 locations between 1991 and 1999, even though <br />daily operations were constrained during the time <br />series of repeat measurements. <br /> <br />. Schmidt and others (2004) conducted geomorphic <br />mapping from air photos and land surveys for the <br />predam and postdam periods. They estimated the <br />loss of sand to be about 25% of the area typically <br />exposed at base flow in predam photographs, but <br />estimates range from 0% to 55% depending on <br />study reach and method of analysis. Their studies <br />further suggested that loss of the sandbar area <br />continued at a relatively steady rate between 1983 <br />and 2002, despite constraints on daily operations <br />imposed after 1991. <br /> <br />Importance of Continuous Long-term <br />Sediment-transport Data <br /> <br />Because of a lack of continuous data on sediment <br />inputs and export that would have allowed for a sedi- <br />ment budget based on measured data, the EIS study <br />team used stable sand-transport rating curves. Stable <br />rating curves assume that for any given flow there is a <br />single value for the corresponding sand concentration <br />and, therefore, a predictable sand-transport rate related <br />to flows released from Glen Canyon Dam. The recent <br />