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<br />100 <br /> <br />101 <br /> <br />Table 7. Water Depth and Velocity Used for Spawning by Warm-Water <br />and Cool-Water Fish <br /> <br />of these depletions are from irrigation and associated uses (U.S, Water <br /> <br />Resources Council. 1971). These depletions often occur in rather small <br /> <br />amounts but cumulatively can have a large impact overall. Further re- <br /> <br /> Depth Velocity <br />Species (meters) ( feet) (em/see) (feet/see) <br />Paddlefish variable variable 49-91 1.6-3.0 <br />Shove1nose sturgeon 0.3-0.9 1.0-3.0 75-150 2.5-4.9 <br />Creek chub -- -- 49-91 1.6-3.0 <br />Longnose dace 0.03-0.3 0.1-0.7 15-45 0.5-1.5 <br />Longnose sucker 0.2-0.3 0.7-1.0 31-45 1.0-1.5 <br />White sucker 0.2-0,3 0.7-1.0 31-45 1.0-1.5 <br />Shorthead redhorse 0,3-0,9 1.0-3.0 31-61 1. 0-2. 0 <br />Smallmouth bass 0.9-1.8 3,0-5,9 11 0.36 <br />Largemouth bass 0.3-1. 8 1.0-5,9 0 0 <br />Walleye 1. 2-1.5 3,9-4.9 0-50 0-1.6 <br />Sauger 1.2-1.5 3.9-4,9 0-50 0-1.6 <br /> <br />duct ions are anticipated for the system in the near future, For example. <br /> <br />the U.S. Water Resources Council estimated that the water exported <br /> <br />from the Green River will increase from 0.12 to 0.65 million acre-feet <br /> <br />and on-site depletions will increase from 0.87 to 1.67 million acre-feet <br /> <br />between 1965 and 2020. The Council estimated similar depletions for the <br /> <br />upper main stem of the ColoradO River--from 0,43 to 0,88 million acre- <br /> <br />feet by export and from 0.97 to 1.35 million acre-feet by on-site deple- <br /> <br />tions for the same time period. <br /> <br />At the present time. it is not possible to make many predictions on <br /> <br />the responses of fish to changes in streamflow because the requirements <br /> <br />of many species or the life stage of a particular species may not be known. <br /> <br />Source: K. D. Bovee. The Determination, Assessment and Desi2Q of <br />"In-Stream Value" Studies for the Northern Great Plains Rel!:ion. Final <br />Report. EPA Contract No. 68-01-2413 (Missoula. Mont.. University of <br />Montana. 1974). <br /> <br />It is particularly important to emphasize that quantitative data be ob- <br /> <br />tained on the streamflow requirements by species and for each life sta~e <br /> <br />if predictions of fish responses to changes are to be made with accuracy. <br /> <br />Responses of Macroinvertebrates to Streamflow <br /> <br />Water flows can greatly affect the invertebrates that are a major <br /> <br />source of food for fish. Reduced water flows can limit the abundance <br /> <br />and diversity of swift-water invertebrates. and excessive flows can <br /> <br />scour the substrate and become detrimental (Giger. 1973; Ward. 1976), <br /> <br />A summary of several studies comparing the relationship between water <br /> <br />velocity in riffles and the numbers of bottom organisms shows that the <br /> <br />numbers of organisms can differ considerably in different streams for a <br /> <br />given water velocity (table 8). Large differences can also exist in <br /> <br /> <br />.. <br />.. <br />... <br />.. <br />.. <br />.:: <br /> <br />( <br />'" <br />... <br />,. <br />... <br /> <br />" <br />, <br />, <br />~ <br />. <br />- <br />, <br />. <br /> <br />{ <br />, <br />~ <br /> <br />.. <br />'tf <br />J" <br /> <br />-~ <br />;.~ <br /> <br />i <br />:~ <br /> <br />~~ <br /> <br />j <br />