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<br />46 <br /> <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />ARKANSAS RIVER FROM OTEROIPUEBLO COUNTY LINE <br />TO JOHN MARTIN RESERVOIR <br />CHANNEL CAPACITY AND RIPARIAN HABITAT PLANNING STUDY <br /> <br />4. DOCUMENTATION OF VEGETATI(j)N AND CHANNEL PROBLEMS <br /> <br />4.1 RESULTS OF AERIAL PHOTOGRAPH COMPARISONS OF VEGETATION <br /> <br />Previous studies conducted in the Arkansas River Valley that specifically discussed <br />phreatophytes and their effects include those reported by Bittinger and Stringham (1963), <br />Lindauer and Ward (1968), Lindauer (1970, 1983 1990), Nadler (1978), and Nadler and <br />Schumm (1981). These studies included areas that are specific to this planning study's problem <br />areas. Aerial photography from CWCB (1998), USQA (1999), (Otero County 1975), USACE <br />(1980), and several other sources was utilized during this planning study and are as referenced. <br />The aerial photography from CWCB (1998) and the USDA (1999) was color photography, all <br />other aerial photography reviewed was black and white. Aerial Photographs, that have been <br />numbered 1 - 6 and are incorporated into this report, are sequential from upstream near La Junta <br />to downstream at Las Animas. This report is a review of aerial photography and therefore, the <br />report is limited in the fact that no quantitative measurements of vegetation can be reported and <br />only qualitative descriptions are presented. The effeCt of riparian vegetation, which is primarily <br />salt cedar, on the Arkansas River in southeastern Colorado, is that salt cedar has encroached <br />upon and confines the river to the existing channel. The salt cedar in effect is armoring the <br />channel banks and therefore the position of the channel is maintained even during small flood <br />events. The salt cedar; however, does slow overbank flood flows and is causing significant <br />sediment deposition in the floodplain. <br /> <br />In Channel Problem Area No.1 (Figure 2), yisual comparisons between Otero County's <br />1975 aerial photographs and the 1998 aerial photogt1aphs provided by the Colorado Water <br />Conservation Board found that there is much more "egetation in 1998 that includes trees and <br />herbaceous growth. Vegetative composition in the area was similar to that previously <br />documented. Cottonwood and salt cedar had matured in the area and salt cedar stands were <br />much denser and more extensive in 1998. Dense, new salt cedar growth is very evident and has <br />encroached on reshaped sand bars and on the river channel banks. Although it is difficult to <br />compare the 1975 black and white photos with the ~998 color photographs that are also at <br />different scales, the river channel appears to be similar in width between the 1975 and 1998 <br />photographs and the river has maintained a similar channel configuration. In 1998, salt cedar <br />appears to be much denser in the eastern half of Chrtnnel Problem Area No. 1. This denser <br />growth begins about 1.5 miles downstream of the Highway 109 bridge at La Junta and extends <br />for about 4 miles in length. Vegetation in the upper half of Channel Problem Area No. 1 (Aerial <br />Photograph 1) would cause some slowing of overbank flood flows but this would not be <br />significant. In the lower half of Channel Problem Area No.1, vegetation is dense enough that it <br />would cause flood flows to slow and could cause significant overbank sediment deposition. <br /> <br />Lindauer and Ward (1968:9, Appendix X, 38) selected an area located about 314-mile <br />east of Bent's Old Fort National Historic Site for their Transect Line No.4. Transect 4 is about 2 <br />