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<br />50 <br /> <br />F. ZAMORA-ARROYO ET AL <br /> <br />their riparian corridors (Dynesius & Nilsson, 1994; Nilsson et al., 1997). In south- <br />western United States, flow-regulated riparian zones have been damaged by loss of the <br />natural pulse-flood regime, that formerly washed excess salts from riverbanks and <br />germinated native trees (Briggs, 1996; Busch & Smith, 1995; Poff et aI" 1997; <br />Stromberg, 1998a). On the lower Colorado River, the largest and most altered river in <br />the south-western United States and Northern Mexico, an exotic, salt tolerant shrub, <br />Tamarix ramosissima (salt cedar), in association with native halophytes, has almost <br />completely replaced the mesophytic native forest that historic\\lly dominated the riparian <br />corridor from Grand Canyon to the delta on the Gulf of California (Ohmart et aI" 1988; <br />Busch & Smith, 1995). Loss of Populus fremontii (Fremont's cottonwood) and Salix <br />gooddingii(Goodding's willow) trees and associated epiphytes and understory plants, <br />has lead to a collapse of supporting habitat for numerous species of plants, birds, <br />mammals and reptiles, so that today 45 species in the lower Colorado River ecoregion <br />are listed as sensitive, threatened or endangered (U.S. Bureau of Reclamation, 1996). <br />Deterioration of native habitat on regulated rivers cail be progressive and irreversible <br />(Nilsson et al., 1997). It is not known if restoring elements of a natural flow regime <br />would by itself permit native species to repopulate south-western riparian zones (Briggs, <br />1996). We report on the effects of pulse floods on vegetation in the delta region of <br />the Colorado River, below the last diversion of water at Morelos Dam in Mexico. These <br />discharges began with the filling of the last large reservoir on the river, Lake Powell <br />behind Glen Canyon Dam, in 1981 (Glenn et aI., 1996, 1999). <br />The entire discharge of the Colorado River is considered to be over-apportioned for <br />human use with no water remaining for ecosystem maintenance (Morrison et aI., 1996). <br />However, the flows of arid-zone rivers are inherently variable. The river's dams are <br />operated to keep the large reservoirs full, to accommodate electric power generation, <br />recreation, and storage for downstream water use. Hence, when there is excess <br />runoff in the watershed, large volumes of so-called 'waste spills' are released to the <br />Colorado River delta and upper Gulf of California. Since 1981, the major releases have <br />been associated with ENSO cycles in 1983, 1993 and 1997, which brought above- <br />normal winter or spring precipitation into the lake system (Glantz et aI., 1996; Li <br />& Kafatos, 2000)(Fig. 1). <br />We analysed the effects of river discharge on abundance of vegetation from 1992 <br />to 1999 and characterized the species composition of existing vegetation using remote <br />sensing and ground methods. We found that pulse floods have reestablished cohorts of <br />native trees in a 100 km stretch of the riparian zone of the delta, and that the extent of <br />vegetation cover in this stretch is responsive to flood flows. <br /> <br />Materials and methods <br /> <br />Study area andjlow data <br /> <br />The general study area is the zone of natural (non-agricultural) vegetation in the riparian <br />corridor from Morelos Dam to the mouth of the Colorado River in the Gulf of California <br />(Fig. 2). The main vegetation types and hydrological features of this zone have been <br />described and entered into a Geographic Information System database (Valdes-Casillas, <br />1998), The riparian corridor is confined within 6 m tall, earthen levees that keep flood <br />waters out of adjacent agricultural fields. The corridor is < 2 km wide in the northern <br />stretch as it passes through the agricultural district, then widens to 30 km in the southern <br />stretch as it approaches the ocean. The river in the delta is a series of braided channels <br />interspersed with straight sections which have been dug to facilitate water movement, <br />Our primary interest for the present report is the 100 km (14,316 ha) stretch of river <br />from Morelos Dam to the junction of the Colorado River with the Hardy River which <br />contains a mixture of native trees and shrub vegetation. Below the juncture the river <br /> <br />I <br />t <br />i <br />r <br />i <br />~ <br />I <br />~ <br />~ <br />~, <br />~ <br />p <br />I <br />~ <br />~ <br />I~ <br />~ <br />'if <br />* <br />~ <br />tt <br />f;:' <br />~: <br />% <br />~: <br />~ <br />~ <br />(i <br />t <br />f' <br />~ <br />~ <br />~ <br />~ <br />~ <br />~ <br />~~ <br />~ <br /> <br />REGENERATION OF TREES IN RESPONSE TO FLOOD RELEASES <br />2??oo <br /> <br />51 <br /> <br /> <br /> <br />o <br /> <br /> <br />1970 <br /> <br />1990 <br /> <br />2000 <br /> <br />1980 <br />Year . <br /> <br />Figure 1. Annual water releases from the United S . , <br />the Southerly International Boundary Th's ,tates .to ~exlco In the Colorado River below <br />water and flows to the Gulf of Califo~ia ~:;~g~n~ staCtJon IS bel~w the last ?ive;-;ion point for <br />g e olorado River delta npanan zone. <br /> <br />1960 <br /> <br />carries saline agricultural drain water to th . <br />native trees. . e sea and IS apparently too saline to support <br /> <br />We used a combination of low-level aerial surve <br />wens to document the vegetation es and ys, ground .~sects and monitoring <br />locations are shown in Fig 2) WetythP hI yddrology of this nver stretch (sampling <br />. .. en corre ate past eta' ' <br />events, using satellite images of the delta and fl dV ge no':1 cover With past flow <br />Boundary and Water Commission US De t ow ata prOVided by International <br />measured at the Southerly Internati~n~1 130 ~. of State, EI Paso, Texas, USA. Flows <br />for water, were assumed to flow to the sea u~ ary' 3.~ km b~low ~e last diversion point <br />(AI Goeff, IBWC, pers. comm.). WI a resl ence time In the delta of 3-5 days <br /> <br />~ <br />.~ <br />i <br />f. <br />I, <br />~ <br />t <br />k <br />" <br />~ <br />~ <br />& <br />~ <br />f <br />1\. <br />I <br />I <br /> <br />Aerial SUI'VeyS <br /> <br />We conducted a medium-altitude (lOOOm) 'al <br />documented by oblique videography to ga' aen su~ey on 27 February 1997, <br />. . ' In an overview of geomo hId <br />vegetation of the nparian ecosystem and to rp 0 ogy an <br />during a release event of known m . obse~e patterns of water distribution <br />(150 m) aerial photographic survey o~~~~' This was foll~wed by a low-level <br />releases, using a multiband (red blue and NIR) ad~ ,19199, follOWing 3 years of water <br />2001). ' Iglta camera (DyCam) (Nagler et aI., <br /> <br />DyCam images taken within the nati ( <br />% of bare soil, trees, shrubs and groun;:o~:~ ~~n~ n = 63) were used to. determine the <br />approximately 67 x 100 m ground area Each h e present s~dY. Eac~ Image covered <br />viewing program and overlain with a iliin-li~d O~Oograo ph,was l~dPorted Into a computer <br />, -pOint gn . Land cover class was <br />