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<br />eastern Sierra Nevada stream that has been <br />partially diverted for hydroelectric power <br />production for more than 80 years, stream- <br />flow is considered to be more "important" <br />(Le" is the exclusive source of water) to <br />riparian vegetation at lower, effluent <br />reaches than at higher elevation. influent <br />reaches (Walsh et al. 1987). The objective <br />of this study was to determine instream <br />flow requirements for maintenance of ri. <br />parian cottonwood (Populus spp.) trees on <br />Bishop Creek. To this end. relations of an- <br />nual streamflow to tree ring width, and <br />tree ring width to canopy vigor and pop- <br />ulation mortality were explored. These re- <br />lations were compared for diverted stream <br />reaches with differing valley geomorphol- <br />ogy and hydrology (i.e., effluent versus in- <br />fluent) and for a reach receiving the di- <br />verted flows. <br />Riparian vegetation maintenance mod- <br /> <br />003076 <br /> <br />els are necessary for streams such as Bishop <br />Creel<, !,v.en though the young age of many <br />of the cottonwood trees indicates that di- <br />version has not precl uded cotton wood es- <br />tablishment. The mere presence of cotton- <br />wood trees (albeit at low density in many <br />reaches) cannot be used as an indicator of <br />sufficient flows, because instream flows for <br />recruitment and those for maintenance are <br />two different concerns. Episodic recruit- <br />ment of cottonwoods at Bishop Creek has <br />been facilitated by the periodic presence <br />of sufficient water during appropriate pe- <br />riods in spring. The water becomes avail- <br />able because the storage capacity of the hy- <br />droplant reservoir system is exceeded in <br />wet years. However, subsequent years of <br />low or no flow can result in stress and mor- <br />tality. necessitating the development of in- <br />stream maintenance models for riparian <br />vegetation. <br /> <br />) <br />"'1.(,.", <br />).'0 <br />" <br />I <br />\' <br />\; <br /> <br />STUDY AREA AND SITES <br /> <br />Bishop Creek drains a 180-km' water- <br />shed in the rain shadow of the eastern Si- <br />erra Nevada Mountains, In its upper reach- <br />es, Bishop Creek flows through steep alpine <br />and coniferous landscapes in a glacially <br />carved canyon. over bedrock and glacial <br />till. The stream in the lower reaches is sur- <br />rounded by Great Basin shrub desert and <br />flows through an alluvial fan before en- <br />tering the Owens River Valley. Precipita- <br />tion ranges from ca. 100 em near the Sierra <br />Nevada Crest (ca. 4.500 m elevation) to ca. <br />IS em at the confluence of Bishop Creek <br />with the Owens River (ca. 1,350 m eleva- <br />tion). Most precipitation falls in winter. <br />Natural flows in Bishop Creek are esti- <br />mated at 93 hm3/year. <br />The main fork of Bishop Creek has five <br />hydroelectric power plants (Figure I). Dur- <br />ing dry and normal hydrologic years, most <br />of the water is diverted from the channel <br />into a series of pipelines, penstocks. and <br />reservoirs, and it is used to generate power. <br />At each power plant the water carried in <br />the penstock. plus any water flowing in <br />the stream, is collected in a small reservoir <br />and delivered to the downstream power <br />plant through another penstock. Flows <br />from nearby McGee Creek and Birch Creek <br />(combined watershed size of 65 km') are <br />also diverted into Bishop Creek penstocks. <br /> <br />Flows are ultimately released into the <br />stream channel below the lowermost pow- <br />er plant. In dry and normal years, these <br />release flows have been 99% greater than <br />flows in the diverted reaches between <br />power plants, and in wet years they have <br />been 40% greater (Smith and Nachlinger <br />1987). Annual flow in the diverted reaches <br />has ranged from < 1.25 hm' in dry years <br />to nearly 50 hm' in wet years. Flows in <br />1982 were exceptionally high, with daily <br />flows exceeding the 100-year flood limit <br />for the town of Bishop (>40 m'/s). <br />The study sites were located in four <br />reaches along Bishop Creek. as described <br />below: <br />Reach 2 is between power plants 2 and <br />3 at an elevation of ca. 2.020 m. It is an <br />influent reach in a V-shaped valley with <br />Quaternary till and has a stream gradient <br />of ca. 5% (Simons, Li and Associates 1990). <br />Annual flow volume from 1969 to 1988 for <br />this diverted reach has been ca. 9 hm3, <br />of which 96% has been in the growing sea- <br />son (May-October) (Figure 2). (Pre-1969 <br />flow data are unavailable for this reach and <br />other diverted reaches.) Annual average <br />precipitation is 34 em. The woody riparian <br />community is fairly dense, consisting <br />mainly of black cottonwood (Populus tricho- <br />carpa T. & G.), Jeffrey pine (Pinus jeftreyi <br /> <br />FIGURE 1. <br /> <br />Grev. & BalL), qu <br />uloides Michx.). <br />talis Hook), and <br />cottonwood is <br />within the reach <br />Reach 4 is bet <br />5 at ca. 1,475 m. <br />an alluvial out <br />gradient of ca. 4 <br />eraged ca. 13.6 <br />been in the gro <br />etation is sparse I <br />only scattered pa <br />of cottonwood, bi <br />mont cottonwoo< <br />in the reach. ' <br />Reach 5 is be~ <br />6 at ca. 1.390 mini <br />The upper porti <br />effluent, but in 1 <br />flow is augment' <br />(Hess and Smith <br /> <br /> <br />I~I 2 <br /> <br />Rivers. Volume 2. Number I <br /> <br />January 1991 <br /> <br />J. C. Stromberl <br />