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Last modified
1/26/2010 3:16:33 PM
Creation date
10/12/2006 4:48:50 AM
Metadata
Fields
Template:
Water Supply Protection
File Number
8220.101.10
Description
Colorado River-Water Projects-Glen Canyon Dam/Lake Powel-Glen Canyon Adaptive Management
Basin
Colorado Mainstem
Water Division
5
Date
1/1/2002
Author
Webb-Melis-Valdez
Title
Observation of Environmental Change in Grand Canyon Arizona
Water Supply Pro - Doc Type
Report/Study
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<br />01.296 <br /> <br />sand bars. while not noticing other aspects. such as <br />changes in wildlife populations. These observations <br />must be taken in aggregate to provide an accurate <br />accounting of environmental changes in Grand <br />Canyon. <br />Much has changed along the Colorado River <br />since most of the Old Timers and other historic river <br />runners were in Grand Canyon. The following changes. <br />many of which are supported using photographic or <br />other evidence, are probably significant: <br /> <br />. The low waler temperature, increase in riparian <br />vegetation, lack of substantial sediment in the <br />river, noise from aircraft, and deteriorated air <br />quality are considered the largest changes in <br />Grand Canyon. <br /> <br />The largest changes in the river corridor. other <br />than rapids. were observed just downstream from <br />Nankoweap Creek (mile 52.2-R), and at the mouth <br />of the Little Colorado River (mile 61-L). Elves <br />Chasm (mile 116.5-L). and Tapeats Creek (mile <br />133.8-R). <br /> <br />. The Old Timers saw little evidence of debris fiows <br />before closure of Glen Canyon Dam. The <br />frequency of debris fiows may have increased <br />after the early 1960s. as speculated by Melis and <br />others (1994) and Webb (]996). Certain rapids -- <br />such as Crystal (mile 98.3). Bedrock (mile 130.5). <br />and House Rock (mile 16.9) -- are now more <br />difficullthan in the pre-dam aa. Lava Falls Rapid <br />(mile 179.5), which was always large, also was <br />discussed as having changed. Other rapids are <br />unchanged or are less difficull. <br /> <br />. Erosion of camping beaches used by pre-dam river <br />runners is severe. Now. some formerly popular <br />camping sites are not easily used for camping. <br /> <br />. Fires had a significant impact on the amount of <br />driftwood along the river corridor. Fires were set <br />randomly and specifically at certain popular <br />places. particularly the mouth of Nankoweap <br />Creek (mile 52.2-R) and Tanner Canyon (mile <br />68.5-L). <br /> <br />. Riparian vegetation. mostly tamarisk. is much <br />denser along the river. whereas cottonwoods and <br />tree-form willows decreased in the post-dam era. <br />Tamarisk slowly increased, particularly in the <br />I 940s and 1950s. but accelerated after 1963. <br /> <br />. Perennial marsh vegetation was not observed or <br />photographed along the pre-dam river except near <br />springs. <br /> <br />. Catfish were the most common fish caught in the <br />pre-dam river, allhough rainbow trout were also <br />present. Some of the Old Timers caught native <br />fish, mostly befNe about 1950, and tbe species <br />they observed could not be accurately determined <br />unless the catch was photographed. <br /> <br />. Ducks and other water birds were commonly <br />observed along the unregulated river, but they <br />were not as abundant as they are now. in accord <br />with the findings of Slevens and others (1997). <br /> <br />Other changes mayor may not be significant. if <br />in fact changes even occurred: (I) Bats and some <br />species of birds may have decreased along the river. <br />whereas swallows may have increased. (2) Bighorn <br />sheep possibly are more numerous; they certainly are <br />observed more often now. No changes can be inferred <br />in the population of deer or other large mammals along <br />the river. (3) It is uncertain whether the population of <br />beavers has changed. and otters remain an uncommon <br />sighting. (4) Bothersome insects were common before <br />Glen Canyon Dam. although it is unknown if species or <br />abundances may have changed. <br />Some of the issues raised in this report have <br />significant implications for dam manageml?nt. The <br />increase in frequency of debris flows will hasten a <br />long-postulated change in the longitudinal profile of <br />the river; without dam releases significantly higher <br />than power plant capacity, the river will eventually <br />attain an exaggerated pool-drop configuration. <br />]mplications of such a trend might be that navigation of <br />rapids becomes generally more difficult, and in some <br />cases. the river may become impassable. Continued <br />aggradation of the river channel by coarse sediment <br />delivered during debris fiows will likely fill-in deeper <br />pools above and below rapids. while also enhancing the <br />size of eddies. On the basis of photographic evidence <br />and sedimenl-lransport studies, bars are predicted to <br />continue decreasing in size (Laursen and others, 1976). <br />Tamarisk was increasing despite pre-dam fiooding. <br />Although dam releases could be used to thin some of <br />the population. tamarisk would have become a <br />common, although exotic. resident of Grand Canyon <br />even if the dam had not been buill. Marshes are an <br />artifact of fiow regulation, not a natural feature of the <br />pre-dam environment (Webb, 1996). Native fish may <br /> <br />CONCLUSIONS 31 <br />
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