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SECTIONTWO Environmental Setting <br />sandbars and islands, has been in a west to east, or upstream to downstream, progression. <br />Woodland encroachment has been greatest in the reaches where the greatest flow reduction has <br />occurred, such as the 130 -mile reach of the North Platte and Platte rivers above Lexington where <br />springtime stream flows have been reduced by 85 percent since the early 1900s. Woodland <br />expansion and encroachment has also occurred downstream of the Johnson Power Plant Return <br />i <br />(J -2 Return) near Overton within the study area. In 1938, approximately 24,700 acres of open <br />channel and barren sandbars existed between Overton and Chapman. In 1969, only about 11,000 <br />acres remained, a loss of about 55 percent during the intervening 31 (Sidle et 1989). <br />years al. <br />Most remaining habitat lies between Kearney and Chapman. <br />Trends in channel narrowing and vegetation encroachment occurring over the last 25 years are <br />not as obvious as those occurring in the earlier part of the century (FERC 1998). Lyons and <br />Randle (1988) concluded that the channel widths near Overton had adjusted to the sediment <br />transport regime during 1957 -1983. They concluded that channel width adjustments had also <br />occurred at Odessa and Grand Island and further channel adjustments in the Odessa to Grand <br />Island reach were possible. Currier (1995) and Johnson (1997) provide differing results on recent <br />changes in channel width. <br />Johnson (1994) reported that that the channel fraction of floodplain in the central Platte River <br />upstream of Grand Island has remained stable or increased. Johnson's investigations suggest that <br />this can be attributed to frequent years in which mean June flows ranged between 2,650 and <br />3,000 cfs and relatively high winter flows coupled with cold air temperatures. The winter flows <br />and temperatures favored ice formation, which can effectively scour young plants. Other factors <br />might include low summer flows leading to seedling desiccation, and occasional high summer <br />flows in the range of 17,650 to 26,500 cfs, which likely caused sedimentation and erosion. <br />Johnson (1997) reported that open channel area has been maintained or has increased in most <br />sections of the Platte River in recent years, despite relatively low flows and infrequent peaks, <br />because of the increasing erodibility of the floodplain. The greater erodibility is due to maturing <br />of the vegetation (lower stem density) and higher floodplain surfaces with steep bank angles. In <br />contrast to most segments, channel area has continued to decrease near Grand Island, which may <br />be due to sediment liberated by upstream vegetation removal within the floodplain. Johnson <br />identified vegetation management project as a "strong candidate" for localized vegetation <br />expansion and open channel decline, but indicated that it could have other causes. <br />Currier (1995) documented an ongoing trend towards continued loss of open channel area and <br />wide channel habitats in the 55 -mile reach between Kearney and Chapman. The loss of <br />remaining open channel in this reach ranged from 4 to 41 percent (average of 26 percent) during <br />1988 -1994. River segments that had already narrowed significantly and sites where channel <br />habitat is actively managed declined approximately 17 to 18 percent. Sites that were <br />unobstructed in 1988 aerial videotapes were sampled and compared with 1994 videotapes. At <br />several sites, extensive mid - channel bar formation occurred between 1988 and 1994. These <br />changes occurred during a time that included a relatively low flow period (1990 -1992) which <br />allowed woody vegetation to become established. A relatively high flow event (i.e., 12,000 to <br />16,000 cfs) during June and July 1995 was effective in removing only 4 to 5 percent of the <br />=swim Wbndi—mi Clyde <br />2-6 WFOM7286=11.d. &V1999(9:52 AM)/URSGWCFS/2 !hdW_dl Services' <br />F1 <br />