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Last modified
7/14/2009 5:02:36 PM
Creation date
6/1/2009 11:57:12 AM
Metadata
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Template:
UCREFRP
UCREFRP Catalog Number
9506
Author
Cooper, D. J. and C. Severn.
Title
Wetlands of the Escalante Ranch Area, Utah
USFW Year
1994.
USFW - Doc Type
Hydrology, Water Chemistry, Vegetation, Invertebrate Communities, and Restoration Potential.
Copyright Material
NO
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Invertebrates <br />Introduction <br />Recent research indicates that several invertebrate taxa <br />are important to larval and juvenile fish. The Chironomidae and <br />the crustaceanss Cladocera and Copepoda are important food for <br />these fish. Grabowski and Hiebert (1988) analyzed stomach <br />contents from many species of fish at different developmental <br />stages. Their work was performed during 1987-88 on the Green <br />River in backwater and riverine habitats from Island Park to <br />Ouray National Wildlife Refuge. They reported that chironomids <br />were by far the most frequently encountered prey in the stomachs <br />of all the fish studied. A study conducted by Marsh and <br />Langhorst (1988) of wild larval razorback suckers diet in Lake <br />Mohave and an adjacent backwater at Arizona Bay found that <br />Cladocera and Copepoda made up a greater frequency of the diet <br />than other available taxa. The study by Marsh and Langhorst, <br />which occurred in a lentic as opposed to the lotic environment <br />studied by Grabowski and Hiebert, also found a greater selection <br />of Cladocera than Copepoda in relationship to availability. <br />A key objective of the present study was to determine the <br />suitability of study wetlands along the Colorado, Green, and <br />Gunnison Rivers as habitat-for rearing endangered fish. Three <br />aspects of habitat suitability are hydrologic regime, chemical <br />environment and food availability. The hydrology and water <br />chemistry variables were discussed above, and this section <br />discusses the availability of food. <br />Bulrush, open water-aquatic and alkali bulrush communities <br />occur in the study area as well as river channel and river <br />backwater communities. All were sampled for invertebrates. The <br />river community was used as a control to compare food resources <br />to those in other communities. <br />Our analyses emphasize the following water column <br />invertebrate groups: 1) Cladocera, 2) Copepoda, 3)~Chironomidae, <br />4) all other insects less the Chironomidae, and 5) all other <br />invertebrates which include Gastropods, Cnidaria, Nematoda, and <br />Protozoa. Taxonomic divisions presented for benthic <br />invertebrates are: 1) Chironomidae and 2) other invertebrates <br />which include Gastropods, Nematoda, Odonata, Hemiptera, <br />Ephemeroptera, Coleoptera, and Culicidae. <br />Water column invertebrate data is typically reported as <br />number L'1 while benthic invertebrate densities are typically <br />reported as number m'Z. For the present study benthic data were <br />also converted to L'1 so that the water column and benthos could <br />be compared. When applicable two Y axes are displayed on graphs <br />to include both number L'1 and number m'Z for benthic <br />invertebrates. <br />32 <br />
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