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<br />Final Report <br /> <br />3-48 <br /> <br />September 2000 <br /> <br />Reach 3, about 1,100 ha was present in the portion of the reach between the White River confluence <br />and Pariette Draw and about 760 ha was present in Canyonlands. Irving and Burdick (1995) <br />prioritized these bottomlands according to their value to endangered fishes and concluded that the <br />highest priority bottomlands were in Reach 2 and upper Reach 3 (Escalante Ranch to Pariette Draw). <br />They did not determine the relationship of floodplain inundation to flow. <br /> <br />Several areas along the Green River, including portions of the Ouray National Wildlife <br />Refuge (NWR), Dinosaur National Monument, Canyonlands National Park, and a significant portion <br />of Reach 2 in the Uinta Basin, have been studied to determine the relationship of flow to floodplain <br />inundation (FLO Engineering, Inc. 1996, 1997; Bell et al. 1998; Cluer and Hammack 1999). <br />Figure 3.18 illustrates this relationship in different study areas. The greatest area of floodplain habitat <br />suitable for satisfying the life-history requirements of endangered fishes in the Green River system <br />is located in the Ouray portion of Reach 2. <br /> <br />The investigation of floodplain-habitat inundation in the Ouray portion of Reach 2 by FLO <br />Engineering, Inc. (1996) used the U.S. Army Corps of Engineers HEC-2 step backwater model to <br />estimate water-surface profiles for a segment of river from RK 400 to 427. The model was used to <br />estimate bankfull discharge and the relationship between flow and area of inundation. Under existing <br />conditions at Ouray, the amount of floodplain inundation begins to increase rapidly as flows exceed <br />about 527 m3/s. With existing artificial levees removed, flooding would be initiated at flows between <br />368 and 453 m3/s. Flooding in the Old Charlie Wash area, where a small side channel allows <br />flooding of approximately 250 ha, begins at approximately 368 m3/s. Other floodplain areas have <br />inlet structures that are operational at flows of 85 to 113 m3/s. If 0.6- to 0.9-m-deep side channels <br />were excavated at certain locations, flooding of about 2,185 ha could be initiated in Ouray floodplain <br />habitats at 368 m3/s. <br /> <br />Flooding in the Island Park portion of Reach 2 (RK 530 to 535) was investigated by Cluer <br />and Hammack (1999). They used numeric hydraulic modeling to evaluate the availability of various <br />habitats over a range of flow conditions at this location. Inundated floodplain area increased from <br />about 2 ha at 312 m3/s to about 98 ha at 1,090 m3/s. <br /> <br />Bell et al. (1998) used aerial photography to determine the relationship between flow and <br />floodplain inundation in Reach 2 from Split Mountain Canyon to the White River (RK 396 to 505) <br />and the upper portion of Reach 3 from the White River to Pariette Draw (RK 380 to 396). At <br />566 m3/s, about 2,100 ha were flooded in Reach 2, about 3,500 ha were flooded at 624 m3/s, and <br />about 4,900 ha were flooded at 705 m3/s. <br /> <br />Most of the floodplain habitat in Reach 3 is located in the upper portion of the reach just <br />downstream of the confluences with the White and Duchesne Rivers, and this habitat is contiguous <br />with the extensive floodplain habitats of Reach 2. In the upper portion of Reach 3 examined by <br />Bell et al. (1998), the area of floodplain inundation was 265,425, and 767 ha at 623, 680, and 920 <br />m3/s,respectively, asmeasuredatthe USGS gage near Green River, Utah (Figure 3.18). Downstream <br />of this area, the river channel is more confined because of either resistant geology (Desolation, Gray, <br />