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<br />character of the drainages as a whole. In some cases it was felt that too much vegetation was <br />growing in the drainage to be considered a real channel or the vegetation was not distinctive <br />enough from normal valley bottom and side slope vegetation, considering the variations <br />within those vegetation units. In other cases, some sites that were initially considered <br />questionable were included in the Waters of the United States category. <br />Once all sites were located, they were measured to determine the amount of land <br />included in the Waters of the United States category throughout the site. The amount of land <br />in the Waters of the United States category would determine what action was appropriate <br />with respect to the regulatory structure. <br />Measuring such units is no simple matter as the boundaries between adjacent units are <br />often broad and although the edges may more or less parallel the channel, the actu;d <br />boundary can meander irregularly producing variable widths. The extent of such an area up <br />and down a drainageway is more easily defined than the width. Boundaries between units <br />along the drainageway are often defined by topographic changes in stream gradient or <br />changes in rock types or the configuration of the valley bottom. But the edges of such units <br />where they meet side slope vegetation are often vague, especially where the vegetation on the <br />side slopes differ little from the vegetation along the channel (e.g. east and west faring <br />slopes along a northward trending drainage). <br />Furthermore, with highly intermittent streams many species found in the bottom of <br />the valleys can be similar to those that are found on the side slopes above the draicage, <br />irrespective of slope aspect or drainageway orientation. In a sense, such drainagew;rys do not <br />necessarily form a separate vegetation unit but are the transition zone between adjacent slope <br />vegetation units. <br />The vegetation in such situations can be a blend of the vegetation found on adjacent <br />slopes plus a few other species that prefer the somewhat more moist conditions of the <br />drainageway. In those cases, deciding what is Waters of the United States and what is not <br />becomes a value judgement based on how different the vegetation is from side slope <br />vegetation and how many distinctive species are found in those areas but not gener;rlly found <br />on the side slopes. Once again, this forms a spectrum from highly distinctive (e.g. cattails <br />and willows in the drainageway with cactus and Juniper on adjacent slopes) to a di:;tinction <br />that may be defined by slightly larger Rocky Mountain Maples or slightly more Poison Ivy in <br />the drainageway than is found on the side slopes. <br />In marginal situations, the nature of the drairtage channel and the soils were used to <br />decide. If the drainage channel was present, but had vegetation (anything from grass to small <br />trees) growing in the path the site was rejected. But if the drainageway was as described and <br />the soils appeared to be wet throughout most of the year then it was included as Waters of <br />the United States .Water seeps and small springs, especially if present in August and <br />September, were always included as Waters of the United States sites. <br />Waters of the US Study Menzer Quarry Page 2 <br />