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<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~~~ ~
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<br />5,00~ .f
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<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 ::
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<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 ~
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<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 />
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