Laserfiche WebLink
1. Background. Low survival can be a major limiting factor during earl <br />life stages. When recruitment does not replace adult mortality, wild <br />stocks decline in numbers. For example, Colorado River squawfish and <br />humpback chub stocks are considered to be low but stable in the upper <br />basin. To protect these stocks and increase their numbers, fishways <br />will be constructed to provide passage over dams into historic habitats. <br />In addition, stream flows needed to maintain vital habitats for both <br />species will be defined. <br />Although spawning has been documented, recruitment of wild razorback <br />suckers is low or non-existent. Therefore, attempts will be made to <br />enhance flooded bottomland habitats with the goal of increasing survival <br />during early life stages to aid natural recruitment. Evaluation of <br />these sites as nursery areas may require stocking naturally spawned <br />larvae into protected (predator-free) sites as recommended-by Dowling <br />and Minckley (1993) in Lake Mohave. <br />2. Guidelines for Maintaining Genetic Diversity in Wild Larval Fish to be <br />Stocked in Protected Environments. Larval fish should be collected from <br />or near a known spawning site in a suspected historic nursery area. <br />Temporal sampling of larvae should be made throughout the natural <br />spawning period (Tyus and Karp 1991). For example, collections could be <br />made weekly using light traps. An attempt should be made to collect <br />equal numbers of larvae during each collection. Standardized techniques <br />should be used during all collections so that mortality of larvae during <br />capture and handling is similar among collections. Ideally, larvae from <br />each collection should be marked. Batch-marking techniques for larval • <br />fish are available through food additives but they require lethal <br />sampling. <br />3. Genetic Characterization of Fish Produced in Protected Environments. If <br />wild fish reared in protected habitats are genetically similar to the <br />wild spawning stock, they can be reintroduced near the spawning site. <br />The number should not exceed 10 per cent of the spawning population. <br />All released fish must be identifiable by a unique mark or tag so they <br />can be monitored in the future. <br />If only a few larvae survive in the protected environment or the genetic <br />characterization indicates that the surviving fish originated from only <br />a few parents, the fish should not be stocked. Dispose of-such fish in <br />accordance with guidelines in Section VI.B. <br />D. Hybridization. Hybridization has important management and evolutionary <br />consequences. Hybridization increases when allopatric populations are placed <br />into sympatry through human activities and when sympatric populations <br />inhabit altered environments (Both et al. 1987). No hybridization has been <br />documented in the Colorado squawfish. However, hybridization has been <br />documented for razorback suckers and the endangered Gila sp. in the Upper <br />Colorado River Basin. Pallid sturgeon may be hybridizing with shovelnose <br />sturgeon in the Mississippi River, and bull trout are known to hybridize <br />12 0