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Tree Physiology 23, 1113 -1124 <br />2003 Heron Publishing — Victoria, Canada <br />Ecophysiology of riparian cottonwoods: stream flow dependency, <br />water relations and restoration <br />STEWART B. ROOD, 1,2 JEFFREY H. BRAATNE3 and FRANCINE M. R. HUGHES <br />Department of Biological Sciences, University of Lethbridge, AB TIK 3M4, Canada <br />Author to whom correspondence should be addressed (rood @uleth.ca) <br />Department offish and Wildlife Resources, University of Idaho, Moscow, ID 83844 -1136, USA <br />Department of Geography, University of Cambridge, Cambridge CB2 3EM U.K. <br />Received October 17, 2002; accepted March 29, 2003; published online October 1, 2003 <br />Summary Cottonwoods (Populus spp.) are adapted to ripar- <br />ian or floodplain zones throughout the Northern Hemisphere; <br />they are also used as parents for fast - growing hybrid poplars. <br />We review recent ecophysiological studies of the native cotton- <br />woods Populus angustifolia James, P. balsamifera L., P. delt- <br />oides Marsh., P. fremontii S. Watson and P. trichocarpa T. & G. <br />in North America, and P. nigra L. in Europe. Variation exists <br />within and across species and hybrids; however, all riparian <br />cottonwoods are dependent on shallow alluvial groundwater <br />that is linked to stream water, particularly in semi -arid regions. <br />This conclusion is based on studies of their natural occurrence, <br />decline following river damming and dewatering (water re- <br />moval), water relations, isotopic composition of xylem water, <br />and by the establishment of cottonwoods along formerly bar- <br />ren natural channels after flow augmentation in response to the <br />conveyance of irrigation water. When alluvial groundwater is <br />depleted as a result of river dewatering or groundwater pump- <br />ing, riparian cottonwoods exhibit drought -stress responses <br />including stomatal closure and reduced transpiration and pho- <br />tosynthesis, altered 13C composition, reduced predawn and <br />midday water potentials, and xylem cavitation. These physio- <br />logical responses are accompanied by morphological re- <br />sponses including reduced shoot growth, altered root growth, <br />branch sacrifice and crown die -back. In severe cases, mortality <br />occurs. For example, severe dewatering of channels of the <br />braided Big Lost River in Idaho led to mortality of the narrow - <br />leaf cottonwood, P. angustifolia, and adjacent sandbar willows, <br />Salix exigua Nutt., within 5 years, whereas riparian woodlands <br />thrived along flowing channels nearby. The conservation and <br />restoration of cottonwoods will rely on the provision of river <br />flow regimes that satisfy these ecophysiological requirements <br />for survival, growth and reproduction. <br />Keywords: Populus. <br />Introduction <br />Cottonwoods (Populus spp.) occur in riparian zones (river val- <br />ley floodplains) throughout the Northern Hemisphere (John- <br />son 1994, Braame et al. 1996, Naiman and 136camps 1997). <br />Along with willows ( Salix spp.), cottonwoods are ecological <br />pioneers that colonize barren riparian sites, and in semi -arid <br />environments they are the dominant and often exclusive ripar- <br />ian tree species (Rood and Mahoney 1995, Scott et al. 1997, <br />Patten 1998). In wetter regions, such as eastern North America <br />and central Europe, cottonwoods are followed in succession <br />by other hardwoods, and in the Pacific region of North Amer- <br />ica and boreal regions of North America and Europe, they are <br />followed by conifers (Johnson 1994, Polzin and Rood 2000). <br />Riparian cottonwoods provide stream -bank stabilization <br />and wildlife habitat, contribute to aquatic ecosystems, and pro- <br />vide the parental genotypes for natural and artificial inter - <br />specific hybrids ( Eckenwalder 1996, Stettler et al. 1996). Nat- <br />ural hybrids are important for ecosystem biodiversity <br />(Schweitzer et al. 2002, McIntyre and Whitham 2003), and ar- <br />tificial intersectional hybrids often grow vigorously and <br />provide fiber, fuel and wood products. However, cottonwood <br />forests are particularly vulnerable to degradation of riparian <br />zones as a result of livestock production, tree harvesting for fi- <br />ber and fuel, and clearing for agriculture, human settlement <br />and transportation corridors (Rood and Mahoney 1990, Patten <br />1998, Muller et al. 2002). <br />River damming and water diversion have further contrib- <br />uted to the collapse of cottonwood populations along many <br />rivers (Rood and Mahoney 1990, Braatne et al. 1996). The de- <br />cline of cottonwoods downstream from dams prompted us to <br />review the dependency of riparian cottonwoods on stream <br />flow and the consequences of dewatering (removal of water) <br />on cottonwood water relations. We focus on studies conducted <br />after 1990, thereby complementing previous reviews of cot- <br />tonwood water relations (Blake et al. 1996, Smith et al. 1998), <br />impacts of damming (Rood and Mahoney 1990, Friedman et <br />al. 1998, Nilsson and Bergren 2000), and life history and con- <br />servation ( Braatne et al. 1996, Karrenberg et al. 2002). We <br />have adopted the taxonomic treatment of Populus described by <br />Eckenwalder (1996). <br />t This paper was among those presented at the /7th North American Forest Biology Workshop "Rocky Mountain ecosystems: Diversity, com- <br />plexity and interactions, " sponsored by the Tree Physiology and Forest Genetics working groups of the Society ofAmerican Foresters and held <br />at Washington State University, Pullman, WA. <br />