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Last modified
7/14/2009 5:02:36 PM
Creation date
5/22/2009 7:23:55 PM
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UCREFRP
UCREFRP Catalog Number
9490
Author
U.S. Fish and Wildlife Service.
Title
Final Environmental Assessment for Procedures for Stocking of Nonnative Fish Species in the Upper Colorado River Basin.
USFW Year
1996.
USFW - Doc Type
Grand Junction.
Copyright Material
NO
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1 <br /> recovery, billions of dollars of water development and subsequent <br /> economic growth could be impacted. The ability of the Recovery Program <br /> to serve as a reasonable and prudent alternative for water development <br />was reduced in 1996. One reason for this was the lack of action to <br /> address nonnative fish problems and implement solutions. Stocking <br /> procedures that contribute significantly towards the recovery of the <br /> fish will, in part, allow the Recovery Program to serve as a reasonable <br /> and prudent alternative for water development. Stocking procedures <br /> that do not adequately address the nonnative fish issues will not serve <br /> as a reasonable and prudent alternative. <br /> 2. Aquaculture Industry: Most fish stocked into private ponds come <br /> from privately owned aquaculture facilities. Aquaculture facilities <br /> produce fish for stocking as well as for consumption. Some facilities <br /> serve as a middle man, acquiring fish from other locations for stocking <br /> into private ponds. Species commonly so]d by these facilities include <br /> rainbow trout, channel catfish, largemouth bass, bluegill, <br />mosquitofish, and triploid grass carp. Ponds stocked with warmwater <br /> fish usually do not require annual stockings; some rainbow trout waters <br /> require stocking each year. Markets for triploid grass carp are <br />increasing throughout the West, due to its' ability to control <br /> vegetation. Warmwater fish stocking in the last five years occurred in <br /> four percent of the ponds along the Colorado River representing 20 <br /> percent of the surface acres. <br /> 3. Private Ponds: Mitchell (1995) identified 308 ponds representing <br /> 878 surface acres along the Gunnison and Colorado rivers; a few ponds <br /> also exist along the White and Yampa rivers. For comparative purposes, <br /> Harvey Gap Reservoir is 196 surface acres and Taylor Draw Reservoir on <br /> the White River is 615 surface acres. On the Colorado River, 73 <br /> percent of the ponds are privately owned and 44 percent of the ponds on <br /> the Gunnison River are privately owned (Mitchell 1995). Nine percent <br /> of warmwater anglers surveyed in western Colorado reported that they <br /> fished in private ponds (Colorado Division of Wildlife 1996). Only one <br />pond owner that reported along the Gunnison River indicated that his <br /> pond was used for fishing, and that was for rainbow trout. For ponds <br /> on the Colorado River, fishing was reported in ponds representing about <br /> 105 surface acres. Twenty-three surface acres contained only <br /> largemouth bass, bluegill, and/or black crappie. Many of the others <br /> contained channel catfish, in addition to largemouth bass, bluegill, <br /> and/or black crappie. At least one pond reported that it contained <br /> grass carp. The survey did not include the Yampa or White Rivers. <br /> Mapping the floodplain revealed little difference (only a few inches in <br /> elevation) between the 50- and 100-year floodplains (Colorado Water <br /> Conservation Board 1995; Appendix D). The boundaries of these two <br /> floodplains generally overlap. Mitchell (1995) surveyed pond owners, <br /> in part, to determine what ponds contained fish. Of the 246 ponds <br />~j Mitchell surveyed between Palisade and Loma, Colorado, 55 were above <br /> the 100-year floodplain, none were located between the 50-100 year <br /> floodplains, 55 were between the 10-50 year floodplain, and 136 were <br /> below the 10-year floodplain. For the Gunnison River between Delta and <br /> 28 <br />j <br />l.i <br />
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