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<br />I <br />fi <br /> <br /> <br /> <br />,r_o, <br /> <br />il <br />fa <br />fI <br /> <br />[I <br />II <br />fa <br /> <br />[' <br />il <br />II <br />ra <br />(I <br />I <br />LI <br />;* <br />I <br />~'I <br />.1 <br />I. <br /> <br />3. Stocking Risk Assessment <br /> <br />Managers have been stocking native fish in the 10werColorado River for over two decades. The reasons <br />have varied. The flannelmouth sucker was one of the first stocked (1976). Wild flannelmouth suckers were <br />captured and translocated for black fly abatement. Some years later razorbacks were stocked for the same <br />reason. Bonytail were stocked into Lake Mohave to augment an existing population and stocked downstream to <br />reestablish the species in Lake Havasu. Stocking protocols for the razorback sucker have been similar, to <br />augment and reestablish populations, but they have also been stocked for mitigation purposes. <br />The choice of stocking sites has been generally driven by logistics, politics, and convenience. The goal of <br />stocking Lake Mohave was population specific but sites varied all over the reservoir. The ultimate goal was to <br />augment existing communities. Fish were stocked adjacent to rearing areas and at common access points. The <br />same was true for bonytail. <br />Stocking downstream of Davis Dam has generally depended on formal or infonnal agreements among state <br />and federal agencies. Federal listing of the razorback sucker, bonytail, and Colorado pikeminnow has caused <br />its own unique challenges concerning the protection afforded the species under the Endangered Species Act. <br />Precedents have been set for razorback sucker and bonytml, since both now exist in the river. However, <br />differences in philosophy and issues pertaining to legal status have prevented the Colorado pikeminnow from <br />being reintroduced. How these differences will play out only time will tell. <br />To our knowledge, no attempt has been made to analyze stocking locations for any of the endangered fishes <br />in the lower basin. The question of what is the most secure reach of river for these fish to my knowledge has <br />not evaluated. More often than not, fish are stocked at the shortest route between the rearing pond or hatchery <br />to the closest boat ramp. Documentation of sucker passage through Davis Dam indicates this approach may <br />not be prudent. <br />The advent of Global Infonnation System (GIS) programs and data bases provides a robust method of <br />assessing habitat types. A . simple stocking assessment model was developed as an example of how this <br />technology could be used to best determine where fish should be stocked to optimize their chances for survival. <br />Susan Broderick and Debra Callahan (oral presentation 2000) developed a stocking risk assessment for the <br />lower Colorado River using ArcView GIS, ArcView Spatial Analyst, and ArcView Model builder. The <br />programs created a visual map that prioritized river reaches based on known survival risks such as: location of <br />diversions, type of dam withdrawal (surface or hypolimnetic), presence and surface area oflarge backwaters, <br />length of unobstructed river reach, and recent occurrence of razorback sucker. <br />They categorized or ranked specific reaches of river using a 1-6 rating system; 1 being poor and 6 being the <br />best chance for survival. Lake Mead and upper Lake Mohave received the highest ranking, a 6. The reach <br />below Davis Dam including upper Lake Havasu, received a ranking from 5-6. Lower Lake Havasu <br />downstream to Parker Dam received a poor rating of 2. The model can be easily modified or updated. Figure <br />2.1 (fold-out) shows the color coded representation for the reach between Davis and Parker Dams. If you have <br />any questions, please contact either Susan (303-445-2235) or Debra (303-445-2235). <br /> <br />22 <br />