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<br />5Z <br /> <br />F. ZAMORA-ARROYO ET AL <br /> <br /> <br /> <br />.-.-' <br />.-.-.- <br /> <br />MEXICO <br /> <br />~U'C <br />"'4J"co - <br /> <br /> <br />" <br /> <br />. <br />10km <br /> <br />Figure 2. Location of study sites in the Colorado River delta, Mexico. The gray area is the stretch <br />of riparian corridor between the levees which supports native trees, the main focus of this study. <br />The stripped area below the native tree zone is a mixture of habitat types, including fresh water <br />and intertidal marshes, mud and salt flats, and vast thickets of Tamarix ramosissima. Triangles <br />denote sites where ground transects were established to quantify vegetation; place names are the <br />settlements (access points) nearest each transect. Closed circles denote sites where well points <br />were established to monitor the depth and salinity of the water table under the riverbed. <br />Numbered line segments show where strings of digital DyCam images were acquired during <br />a low-level fight over the delta in May 1999. <br /> <br />visually scored at each intersection to determine % cover of each class. Results were then <br />ground-trUthed at nine locations (see Nagler et al., 2001, for details). Native trees <br />> 6 m height could be distinguished from other vegetation based on the length of <br />shadows they cast in the photos. Shrubs (mainly T. ramosissima) were defined as plants <br />that had definite size and shape but were < 6 m based on shadow length. Groundcovers <br />were green areas on photographs in which individual plants could not be distinguished. <br />Bare soil and water were identified by color (soils were light-colored whereas water <br />appeared nearly black in multi-band images). <br /> <br /> <br />REGENERATION OF TREES IN RESPONSE TO FLOOD RELEASES <br /> <br />53 <br /> <br />Normalized difference vegetation index (NDVI) values could also be calcuated <br />for each image using the ratio of Red and IR bands (Nagler et aI., 2001). A wider <br />set of images (n = 84)(Fig. 2) established a high coefficient of determination <br />(r2 = 0.83) between percent vegetation cover and reflectance-'based NDVI values cal- <br />culated for the aerial photographs. This relationship was used to calibrate satellite <br />images of the delta to determine percent vegetation cover over past years. <br /> <br />c' <br />el <br />W <br />t'v <br /> <br />Satellite imagery <br /> <br />(' <br /> <br />We acquired six Thematic Mapper 5 (TM) images showing summer vegetation pat- <br />terns covering before- and after-periods of release events from 1992~ 1999. Images for <br />Path 38, Row 38 were selected for cloudless day in May 1992, July 1994, June 1996, July <br />1997, June 1998, and May 1998. An additional image was obtained for 23 Febmary <br />1997, to delineate areas inundated by flood flows during a release event. The Febmary <br />1997 and May 1999 images were taken within 3 weeks of aerial surveys over the delta. <br />Images were preprocessed and georectified by EarthSat, Inc., Rockville, MD, U.S.A. <br />Digital numbers were converted to exoatmospheric reflectance values (0-1) using <br />archived radiance data for each scene and sun angle functions calculated from solar <br />azimuth and angle based on date, time of day and attitude and longitude, using ENVI <br />software (Christopher Jengo, EarthSat, Inc., pers. corom.). The scenes were masked to <br />include only the area of interest depicted in Fig. I, and NDVI values were calculated <br />using ERDAS software. <br /> <br />o...J <br /> <br />Change analyses <br /> <br />There was a near 1 : 1 correspondence between NDVI values calculated for water, soil <br />and vegetation on a May 1999 satellite image of the delta and on DyCam images <br />obtained by low-level overflight the same month (Nagler et aI., 2001) and NDVI values <br />for different land cover classes were nearly identical over the different TM <br />images (coefficient of variation < 10%) from 1992 to 1999 (Fig. 3). Hence, we <br />used the formula relating % cover to NDVI, determined for DyCam images, to estimate <br />% cover 'on TM images (y = 180x + 7'95, r2 = 0'837) (Nagler et aI., 2001). <br /> <br />~o <br /> <br /> <br />-1 <br /> <br />Min. Water Mean Soil Max, <br /> <br />Figure 3. Means and standard deviations (error bars) of ND~ values for similar. landscape <br />features on 1992-1999 TM images of the delta. Max and Mm refer to the maxunum and <br />minimum NDVI values on each image; Mean refers to the mean NDVI values of all pixels on each <br />image; and water and soil refer to NDVI values f~r five randomly-selected water and soil areas on <br />each image. Differences among years for SOil, water and mean NDVI values were not <br />significant at p < 0,05 (max. and min. values could not be compared among years as there was <br />only one value available per image). <br />