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1114 <br />Stream flow dependency <br />ROOD, BRAATNE AND HUGHES <br />The determination of a causal relationship between river <br />damming and dewatering and cottonwood decline is based on <br />evidence that cottonwoods are dependent on water originating <br />from stream flow. There are five lines of evidence supporting <br />this association (Table 1). <br />Natural occurrence <br />In semi -arid regions where low precipitation limits woody <br />vegetation, cottonwoods are restricted to riparian zones where <br />supplemental water is provided by a stream or river (Braatne et <br />al. 1996). The extent of cottonwoods away from the river is re- <br />lated to elevation rather than distance. Trees are restricted to <br />streamside bands up to 3 to 4 in above the base stage of the <br />river in late summer (Stromberg et al. 1996, Horton et al. <br />2001b). <br />Damming and dewatering <br />Studies along dammed rivers further indicate cottonwood de- <br />pendency on stream flow (Table 1; Rood and Mahoney 1990, <br />Friedman et al. 1998, Patten 1998). Cottonwood populations <br />downstream from many dams have declined, especially in re- <br />sponse to dewatering as a result of irrigation during the hot, <br />dry period of mid- to late summer. <br />The Big Lost River provides a vivid demonstration of the <br />negative impacts of dewatering on riparian woodlands (Fig- <br />ure 1). This river flows in braided alluvial channels in Idaho <br />(latitude 43.60 N, longitude 113.5° W): some of the channels <br />are used to convey irrigation water (R.M. Lundy, Big Lost <br />Table 1. Evidence that riparian cottonwoods are dependent on stream flow <br />River Irrigation District, unpublished report, 1993), whereas <br />other channels are entirely dewatered during the irrigation <br />period. Narrowleaf cottonwoods (P. angustifolia James) and <br />sandbar willows (Salix exigua Nutt.) died along the diverted <br />channels but continued to thrive along the flowing channels <br />(Figure 1). Mortality occurred over about 5 years of summer <br />dewatering, with complete mortality by 1993. The period from <br />1987 through 1991 included a sequence of dry years that <br />prompted increased dewatering, which contributed to drought <br />stress (R.M. Lundy, unpublished report, 1993). Lundy con- <br />cluded that alluvial groundwater is reliant on stream flow and <br />that mortality of cottonwood and willow occurs within 5 years <br />of stream dewatering. <br />There are several other reports of cottonwood decline fol- <br />lowing damming, confirming dewatering as a cause of cotton- <br />wood decline (Braatne et al. 1996, Mahoney and Rood 1998, <br />Patten 1998). Additional factors contributing to cottonwood <br />decline include livestock grazing and trampling, invasion by <br />exotic weeds, an excess of beaver or large ungulates (elk), and <br />herbicide application and drift (Braatne et al. 1996, Patten <br />1998). <br />Supplemental flows <br />Dewatering can result in cottonwood decline, whereas the pro- <br />vision of supplemental water can promote cottonwood forests. <br />Irrigation canals are often unlined, permitting water to infil- <br />trate adjacent riparian zones. Additional vegetation, often in- <br />cluding cottonwoods and willows, frequently follows along <br />these canals. Natural channels are also used to convey irriga- <br />tion flows. Such channels may be intermittent (irregular flows) <br />Evidence <br />Description <br />References <br />Natural occurrence <br />In semi -arid regions such as prairies, cotton- <br />Widespread observation <br />woods are restricted to riparian zones, and <br />upland areas are naturally treeless. <br />Dewatering <br />Depletion of alluvial groundwater as a result of <br />Figure 1. Rood and Mahoney 1990, Smith et al. 1991, <br />reduced stream flow following damming or <br />Stromberg and Patten 1992, Busch and Smith 1995, <br />diversion, groundwater pumping or interruption <br />Rood et al. 1995, Pautou et al. 1997, Scott et al. 1999, 2000, <br />of the stream to groundwater transfer has <br />Somogyi et al. 1999, Horton et al. 2001 b, <br />resulted in cottonwood decline. <br />Amlin and Rood 2003 <br />Supplemental water <br />Cottonwoods colonize banks along irrigation <br />Figure 2; widespread observation <br />canals and become established following flow <br />augmentation of natural channels that were <br />previously treeless as a result of intermittent <br />flows. <br />Physiological correlations <br />Morphology and physiology are correlated <br />Stromberg and Patten 1990, 1992, 1996, Smith et al. 1991, <br />with flow characteristics over time, across <br />Busch and Smith 1995, Willms et al. 1998, <br />treatments or in comparisons among streams. <br />Scott et al. 1999, 2000, Horton et al. 2001 b, 2001 c, <br />Amlin and Rood 2003, Cooper et al. 2003 <br />Isotopic composition <br />110 /160 and 2H /'H ratios of cottonwood xylem <br />Dawson and Ehleringer 1991, Busch et al. 1992, <br />water are sometimes similar to groundwater <br />Kolb et al. 1997 (Acer negundo), Snyder and Williams 2000, <br />originating from stream water. <br />Lambs and Berthelot 2002, Lambs et al. 2002, <br />Cooper et al. 2003 <br />TREE PHYSIOLOGY VOLUME 23, 2003 <br />