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<br />INTRODUCTION <br />Riparian vegetation plays an important role in riverine ecosystems. Riparian vegetation <br />offers structural cover for various animals, especially juvenile fish, macroinvertebrates and birds <br />(Naiman and Decamps 1997), and contributes detritus to the adjacent river channel (Neckles and <br />Neill 1994). This detritus provides nutrients for periphyton, bacteria, and detrivores in the <br />immediate area and at downstream sinks (Vannote et al. 1980). Characteristics of detritus, such <br />as its rate of decomposition, can affect the productivity of the entire ecosystem (Lindeman 1942, <br />Ovington 1962). If riparian species exhibit different morphologies or rates of decomposition, <br />their distributions could influence the spatial patterns of habitat quality and productivity (Lewis <br />1998). Riparian vegetation also moderates hydrologic events (Hickin 1984). Above-ground <br />plant tissue provides roughness that reduces water velocity, causing sediment deposition on <br />floodplains (Everitt 1968). Root masses retain bank and floodplain soils, thus providing a <br />medium for infiltration of floodwaters. Riparian vegetation often dampens hydrologic regimes <br />through uptake and release, enabling floodplains to act as natural filters and to remove pollutants <br />from rivers (Mitsch and Gosselink 1986). <br />Flood regime and floodplain topography have a large influence on the distributions of <br />riparian plant species. Thus, floodplain restoration may affect vegetation distributions. A major <br />concern of the Green River Restoration Group is the effect of floodplain restoration on <br />vegetation, particularly the exotic perennial herb Lepidium latifolium (giant whitetop). This <br />noxious weed has become abundant in riparian ecosystems in the American Southwest during the <br />last few decades. Giant whitetop possesses the typical life history characteristics of an invasive <br />exotic plant: it grows rapidly, it colonizes disturbed areas, and throughout the growing season it <br />produces abundant seeds that are easily dispersed by wind and water (USDA 1974). Therefore, it <br />poses a potential problem in agricultural areas where the soil is periodically disturbed. <br />The purpose of this study was to monitor the short-term effects of floodplain restoration <br />on vegetation. We had three major objectives. Our first objective was to develop pre-restoration <br />vegetation maps of restored floodplain sites from two data sources, and to compare the accuracy <br />and efficiency of these two approaches. The second objective was to monitor colonization at <br />restored sites. The third objective was to identify environmental factors that influence whether <br />sites will be colonized by giant whitetop. <br />METHODS <br />Development of a Base Vegetation Map <br />The existence of remotely-sensed data of the Green River in the Uintah Basin provides a <br />tool for examining spatiotemporal vegetation patterns. Different vegetation types have distinct <br />canopy characteristics, such as pigmentation, surface texture, orientation of leaves and branches, _ <br />total biomass, and moisture content (Colwell 1974, Gates et al. 1965, Gates 1970). These <br />characteristics allow us to distinguish among different vegetation types using remotely-senstA <br />data. Classification of aerial photographs has been used to detect vegetation changes in pany <br />riparian systems (Graf 1978, Johnson 1994, Miller et al. 1995; see also Ellis and Woitt?pw ch <br />1989). . <br />21 <br />1 <br /> <br /> <br /> <br />1 <br /> <br /> <br /> <br /> <br />1 <br /> <br />t <br /> <br />'J <br />1 <br /> <br />1 <br />