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Last modified
7/14/2009 5:02:28 PM
Creation date
5/22/2009 7:30:27 PM
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UCREFRP
UCREFRP Catalog Number
6010
Author
Binns, A., et al.
Title
The Planning, Operation, and Analysis of the Green River Fish Control Project.
USFW Year
1964.
USFW - Doc Type
\
Copyright Material
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-8~ <br />In the fall of 1961, it was decided to make comparative tests, <br />under field conditions, of the efficiency of several emulsifiable rotenone <br />products. One of the questions to be answered was the degree to which <br />fairly high water alkalinity might reduce rotenone's distance-length of <br />effectiveness. For this purpose, several test stations, with interspersed <br />cages of live carp, were set up on the Big Sandy River, one of the most <br />alkaline waters to be included in the major project. At that time the <br />stream had a pH of 8.1 to 8.2, total alkalinity of 170 to 240 ppm, and a <br />temperature range of 44 to 56 degrees Fahrenheit. The tests demonstrated <br />that the various chemicals showed no appreciable variations and relatively <br />little loss of efficiency due to alkaline conditions. <br />For additional information it was decided to repeat some of the <br />tests in the spring of 1962. This was done during the week of May 7, prior <br />to the runoff, with three rotenone treatment stations. To simulate the <br />main project's plan, the stations were set ten miles apart, placed in <br />operation at three-hour intervals, and maintained for six hours duration. <br />Observations made during both series of tests on fish-kill time requirements, <br />indicated that it would be advisable. to extend all rotenone introduction <br />periods from six to seven hours. <br />The Refined Rotenone Introduction System <br />From the numerous preliminary chemical treatment tests evolved <br />certain basic facts. For a rotenone concentration of 5 ppm, the float- <br />valve system of flow control and the 3~4 inch dispersal line were satisfactory <br />only when river flows were under 500 cfs. As it was felt that the Green <br />River treatment techniques should be capable of handling flow volumes up <br />to 1400 cfs, some refinements of the original dispersal system were necessary. <br />It was suggested that, with the large water volumes, the overall aspects of <br />rotenone introduction were so gross, that extreme exactitude of low measure- <br />ment was unwarranted. <br />A series of checks were made of rotenone flow rates from 55-gallon <br />barrels. It was indicated that the variation from initial flow to final <br />flow was insufficiently great to justify the complexities and expense of <br />the float-valve control. It was also determined that replacement- of the <br />3~4 inch hose with a one-inch system made it possible to obtain sufficient <br />rotenone dispersion for the maximum workable stream of 1400 cfs. While <br />there was a good probability that some of the upper river stations would <br />not have stream flows of a volume requiring the one-inch capacity equip- <br />ment, for the sake of uniformity and interchangeability, the one-inch system <br />was selected for a standard. Basically, the specifications for a typical <br />treatment station required two 55-gallon rotenone barrels to which was <br />coupled a one-inch capacity yoke. The yoke was composed of three valves, <br />a gate valve on each of the two barrel connections, and a gas valve on the <br />main stem (Figure 3)• .Because the gas valve was adjustable from full <br />open to full close in a quarter turn of its handle, it was ideally suited <br />for fairly exact control of rotenone flow rates. From the yoke, the rotenone <br />was transported across the stream channel by one-inch industrial hose. <br />The hose was purchased in 50-foot lengths with standard pipe couplings <br />attached. A sufficient number of hose sections were coupled together to <br />accommodate each specific stream situation, and two or three 3/4 inch <br />
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