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<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 />l <br />I <br />I <br />I <br /> <br />0[1810 <br /> <br />sediment sorting on the recession. Consequently, deposition can occur in pool areas, <br />sediment may deposit in the middle of the channel, and a low flow channel may not fully <br />develop. <br /> <br />6.3. Historic Changes in Upper Arkansas River Morphology <br /> <br />On the Arkansas River project reach, both sediment load and hydrologic regime have <br />changed over the past 150 years, although not necessarily during similar time frames or <br />in relative magnitudes. Sediment loads have changed as a result of the California Gulch <br />mine tailings contributions, and potentially due to upstream tributary erosion caused by <br />flow augmentations. The caliber of sediment that has entered the system from California <br />Gulch is primarily fine-grained, although some coarse placered material may have been <br />contributed as well. Actual historic, existing, and predicted sediment loads were not <br />available for this study; it is assumed that the implementation of sediment control <br />measures on California Gulch has reduced the sediment inputs relative to the early 20th <br />century. The hydrology of the project reach has historically been affected by flow <br />augmentation, although historic augmentations are not reflective of current management <br />practices (BOR, 1999). Additional human impacts to the river morphology include land <br />use practices, specifically livestock grazing, as well as the impact of the tailings toxicity <br />on riparian vigor and associated bank stability. <br /> <br />To determine the geomorphic evolution of the project reach, aerial photographs dated <br />1939,1957, and 1996 were obtained and evaluated in terms of plan form dynamics and <br />trends in channel width. Flow duration curves were utilized to estimate the frequency of <br />occurrence of hydrologic events that would drive significant channel adjustments. <br /> <br />6.3.1. Sinuosity and Split Flow <br /> <br />Channel planform characteristics are those features of a channel as seen in map view. <br />Channel sinuosity is a measure of stream length versus down valley length, and is a <br />primary planform descriptor. Split flow conditions refer to the presence of multiple <br />channel threads under low flow conditions; this includes locally braided reaches where <br />extensive bar deposits are present, to long segments of multiple, largely separate <br />channels. Channel sinuosity and split flow as determined from aerial photographs dated <br />1939, 1957, and 1996 depict significant changes along the project reach (Tables 6.1 and <br />6.2; Figures 6.1 and 6.2). In general, sinuosity decreases in the downstream direction <br />through the project reach, from a high of 1.25 upstream of California Gulch to a low of <br />1.08 near Balltown. <br /> <br />Subreach I, upstream of California Gulch, experienced an increase in sinuosity from <br />1939 to 1957 and a subsequent decrease from 1957-1996 (Table 6.1; Figure 6.1). This <br />trend reflects the natural dynamics of a multi-channeled system; from 1939 to 1957, the <br />primary channel became more sinuous, which reduced its hydraulic efficiency. In 1992, <br />that channel avulsed into another channel, forming a more efficient, less sinuous thread. <br />This reach is upstream of the California Gulch sediment source. The 1992 relocation may <br />have been in part driven by flow augmentations, although the process occurs naturally in <br />multi-channeled systems. <br /> <br />May 7, 1999 <br /> <br />Fluvial Geomorphological Assessment <br />Upper Arkansas River <br /> <br />Page ]7 <br />