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<br />JARRETT AND TOMLINSON: REGIONAL INTERDISCIPLINARY PALEOFLOOD METHOD <br /> <br />little bucket data have been collected in recent years, severa)-,; <br />extreme rainstorms have been documented in northwestern <br />Colorado since the early 1900s. <br /> <br />4.5. Streamflow Data <br /> <br />Streamflow data for 218 sites in the Yampa River and White <br />River basins were compiled and used to assess extreme flood- <br />ing in the region. U.S. Geoiogical Survey and Colorado State <br />Engineer streamflow records through 1998 are available from <br />the U.S. Geological Survey's NWIS-W Data Retrieval system <br />(http://waterdata.usgs.gov). These data were then used to de. <br />velop an envelope curve of peak discharge versus drainage <br />area for northwestern Colorado. Unit discharge can be used to <br />infer both maximum rainfall intensities and spatial extent of <br />rainstorms [Jamtt, 1990b]; the data were used to develop an <br />envelope curve for unit discharge versus elevation. <br /> <br />4.6. Flood-Frequency Relations <br /> <br />To help facilitate risk assessments of rare floods for dam <br />safety officials and floodplain managers, flood-frequency rela- <br />tions were developed from an analysis of annual peak flows <br />through 1998 for selected streamflow-gaging stations in north- <br />western Colorado where paleoflood data are available. A va- <br />riety of distribution functions and estimation methods are <br />available for estimating a flood-frequeocy distribution [NRC, <br />1999]. Flood-frequency relations normally are developed using <br />a log-Pearson type III frequency distribution [Interagency Ad- <br />visory Committee on Waler Data, 1981] referred to as Bulletin <br />17B (BI7B) and the expected moments algorithm (EMA) <br />[Cohn el aI., 1997; England, 1998J. B17B guidelines were es- <br />tablished to provide consistency in federal flood-risk manage- <br />ment for handling low and high outliers, for recognizing the <br />need for regionaiized skew, and for zero-flow adjustment, for <br />example. <br />EMA is an efficient approach for incorporating historical <br />and paleoflood data and uses the iog-Pearson III distribution <br />[Cohn el aI., 1997; NRC, 1999]. The NRC [1999] recognized the <br />need to follow the spirit of the guideiines such as when using <br />EMA. The EMA is used as the generalization of the conven- <br />tionallog.space method of moments and makes more effective <br />use of historical and paleoflood data in a censored-data frame- <br />work [England, 1998; NRC, 1999]. EMA explicitly iocorpora1es <br />the number of known and unknown discharges above and <br />below a threshold, number of years in the historic/paleoflood <br />period, and knowiedge of the number of years wben no large <br />floods have occurred [Cohn el al., 1997; England, 1998J. The <br />difference between BI7B and EMA is the treatment of historic <br />and paleoflood data [England, 1998]. For B17B the gage record <br />is used to fill in the censored (unknown) floods, whereas EMA <br />computes the expectations for flow data below the threshold <br />and weights this value by the number of censored values [En. <br />gland, 1998]. A comprehensive review of the EMA, censoring <br />thresholds and analyses of contemporary and paleoflood data <br />is provided by England [1998]. <br />For this study, several alternative flood-frequency distribu- <br />tion estimates were determined for the study sites in north- <br />western Colorado using EMA to better use the long paleoflood <br />records. This analysis was done for various combinations of <br />gage and paleoflood data available at each site. Low outliers <br />were adjusted using the B17B procedure to externally elimi- <br />nate low outliers that affected the fit of the upper end of the <br />CUlVe to the data, which is similar to discharge threshold cen- <br />soring [Cohn el al., 1997; Levish el al., 1994; NRC, 1999]. <br /> <br />2967 <br /> <br />Censoring beiow a threshold can account for an assumed dis- <br />tribution not fitting the "true" distribution at a site [NRC, <br />1999J. Low outliers in Colorado often result from modest <br />streamflow diversions for irrigation of hay meadows during <br />low-flow years, but in normal years these diversions have min- <br />imai (<5%) effect on peak flows [Jamll, 1987]. Historicai and <br />paleoflood data also are censored sampies because only the <br />largest floods are recorded. Paleoflood data (magnitude and <br />ages) were incorporated into the flood-frequency analysis to <br />extend the gaged record. In the EMA analysis the paleoflood <br />discharge was specified as a range, and EMA runs were made <br />for 1he range in age (Table 2) for a site. <br /> <br />5. Results <br /> <br />5.1. Paleoflood Investigations <br /> <br />Paieoflobd data from on-site studies of 88 sites throughout <br />the study area are provided in Table 2. Although not all trib- <br />utary streams in the northwestern Colorado were documented <br />(because of inaccessibility to private property), sites were se. <br />iected such that paleoflood data were collected downstream <br />from tributaries on the main stream or similar to "nested" <br />sites. For each site, drainage area, elevation, channel slope, <br />type of PSI (either flood bar (FB) or noninundation surface <br />(NI), width, depth, veiocity, flood discharge corresponding to <br />the maximum PSI (e.g., Figure 6), and sediment-size data, <br />where available, are presented. Site selection was dependent <br />on finding good PSIs (FB and NI) throughout a 50 to 300 m <br />length (length dependent on size of channel). Ideally, each site <br />would have a FE and a NI surface. Sites were primarily in <br />straight, uniform reaches where local aggradation or degrada- <br />tion would be least. General scour appears to have been small <br />during the Holocene. According to Madnle [1991aJ, there has <br />been about a meter of degradation along most the Yampa <br />River during the Hoiocene. Paleoflood evidence along the <br />upper Yampa River primarily was midchannei bars. These bars <br />(islands) were interpreted as erosional remnants of the late <br />Pleistocene channel rather than depositional features, and thus <br />maximum paleofloods using present channel geometry may be <br />slightly overestimated. Some streams have had littie bed ma- <br />terial movement (Table 2), and only NI evidence exists, but if <br />the NI surface is consistent. in the reach of river, then the <br />maximum paleoflood discharge was considered reliable. If a <br />reach of the same channel had similar paleoflood discharges at <br />several sites, the discharge estimate was considered more re- <br />liable. For alluvial channels the discharge was considered less <br />reliable and reflected in an assigned sbort 8ge of 100 years, <br />which is when much of the channel arroyos deveioped in Col- <br />orado [Patton and Schumm, 1975, 1981; Womack and Schumm, <br />1977]. <br />RD data using the criteria shown in Table I also are sum- <br />marized in Table 2. For each site the weathering characteristics <br />for each of the RD methods used, their numerical rating, <br />estimated age, and reliability (range) of age estimates, are <br />provided. Assigning a numerical rating, an age, and range in <br />age for each RD method used is subjective; however, if all <br />methods used suggest similar numerical ratings, then the com- <br />posite age estimate is iikely more reliable. Although individual <br />RD ages are rather crude and may provide different relative <br />ages of a surface, a composite relative age using several meth- <br />ods clearly enables one to distinguish deposits of various ages. <br />Although the error of individual RD ages can be :!:50% [Bir- <br />keland, 1990], composite age is likely more accurate. For use <br /> <br />