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<br />and perhaps other endangered fishes were inventoried, classified, and prioritized <br />using 5 criteria during 1993 (Irving and Burdick 1995). <br /> <br />Bottomland Habitat Sites in the Green River Subbasin. The top ranked bottomland <br />habitat sites in the Green River (32) were located between Pariette Draw and <br />Escalante Ranch (Irving and Burdick 1995; RM 238-310 [RK 383-499]; 6,093 acres <br />[2,466 ha]). Six sites on the Ouray National Wildlife Refuge (RM 249-265 [RK <br />401-427]; 2,265 acres [917 ha]) were ranked either as 1 or 2. Floodplain <br />terraces comprised the vast majority (n = 99 or 75%) of bottomland habitat types <br />in the Green River Subbasin while floodplain depressions comprised the remaining <br />25% of bottomland sites. Four percent of the 132 potential bottomland sites <br />along the Green River were separated from the river by natural levees while 11% <br />were separated by levees constructed by humans. Approximately 20 miles of the <br />Green River consisted of natural and human-constructed levees at 20 sites. <br /> <br />Bottomland Habitat Sites in the Colorado River Subbasin. The top ranked <br />bottomland habitat sites along the Colorado and Gunnison rivers were scattered <br />in four general areas (I rvi ng and Burd i ck 1995): (l) Colorado River between <br />Debeque and Rifle, Colorado (RM 203-240 [RK 327-386]); Grand Valley reach of the <br />Colorado River between Loma and Palisade, Colorado (RM 152-185 [RK 245-298]); <br />Colorado River between McGraw/Hotel Bottoms and the Cisco boat landing (RM 99-110 <br />[RK 159-177]); and the Gunnison River near Delta, Colorado (RM 50.2-54.2 [RK 81- <br />87]). Bottomland habitat sites in the Colorado River Subbasin consisted of 37% <br />floodplain terraces, 21% gravel-pit ponds, and 20% side channels. Natural levees <br />separated 14.6 miles (23.6 kilometers) of the 158 bottomland habitat sites along <br />the Colorado and Gunn i son ri vers wh il e 34.9 mil es (56.3 kilometers) were <br />separated by levees constructed by humans. <br /> <br />Federal agencies own most (75%) of the bottomlands in the vicinity of Brown's <br />Park and a high percentage (58%) of the bottomlands between Escalante Ranch and <br />Brennan Bottom on the Green River (Irving and Burdick 1995). All of the <br />bottomlands on the Ouray National Wildlife Refuge and the majority of bottomlands <br />between Desert Spring and the confluence of the Green and Colorado rivers are in <br />federal ownership. A smaller percentage of the bottomland habitat along the <br />Colorado (15%) and Gunnison (22%) rivers were in public (i.e., federal and state) <br />ownership. The largest proportion of bottomland habitat along the Colorado River <br />in federal ownership (83%) was within Canyonlands National Park. <br /> <br />Obviously, sufficient bottomland habitat is in public ownership along the <br />Colorado and Green rivers so that experimental removal of levees can be evaluated <br />as to zooplankton and benthic invertebrate production and responses by endangered <br />as well as nonnative fishes. Levee removal should be confined to low floodplain <br />terraces in public ownership where thorough evaluations can be made of these <br />efforts. Experiments on public property would preclude high streamflow releases <br />from upstream dams that would cause sociological problems associating with the <br />flooding of private agricultural lands and the production of mosquitoes that <br />could pose human health problems. Leasing of bottomlands in private ownership <br />can be explored if field experiments of floodplain enhancement or restoration are <br />successful on public properties. <br /> <br />17 <br />