|
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River Irrigation District, unpublished report, 1993), whereas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stress (R.M. Lundy, unpublished report, 1993).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 />
|