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current public warmwater fishing in the floodplain is below the 100-year <br />floodplain and would have to be trout only. Localized losses in fishing <br />opportunities would occur, especially during summer months. if <br />alternative fishing locations were not obtained. <br />3. Recovery of Endangered Fishes: The reduction of nonnative fishes <br />escaping into the river would decrease, somewhat, competition with and <br />predation on the endangered fishes. Survival of eggs. larvae. and <br />juveniles of the endangered fishes would slightly increase. External <br />sources of nonnative fishes would no longer compound recovery efforts. <br />Other recovery actions would exhibit measurable positive responsQS in <br />the endangered fish populations. <br />4. Economy: Stocking of private ponds with warmwater fishes would <br />decrease causing impacts to the aquaculture industry and loss of future <br />fishing opportunities in private ponds. Stocking of rainbow trout <br />produced by the aquaculture industry should correspondingly increase. <br />Substitutes--for mosquitofish and grass carp would be in the form of <br />pesticides and herbicides. The change in overall fishing days in <br />Colorado would be minimal. The change in overall fishing days in <br />Colorado would be minimal. This alternative may reduce fishing <br />expenditures by some unknown amount. As an example, if future warmwater <br />fishing opportunities are reduced by 20 surface acres, assuming 100 days <br />fishing/acre at $40/day expenditure, the direct economic impact could be <br />$80,000/year: if reduced by 100 surface acres the direct impact would be <br />$400,000/year. <br />E. Alternative 4. <br />1. Aquatic Biological Resources: Stocking in the floodplain would <br />continue and some escapement would continue to occur. Stocking of ponds <br />in the 10-year floodplain would require berming to FEMA standards. <br />Therefore. because of the cost of such berming, the numbers of new <br />private ponds contributing nonnative fish to the system would not likely <br />increase. Stocking above the 10-year floodplain would allow for the <br />periodic escapement of nonnative fish into the river. These same fish <br />would serve as seed fish for ponds that had been reclaimed, thereby <br />compromising pond reclamation efforts. Because of the problem of fish <br />above the 10-year floodplain and upstream of critical habitat reseeding <br />lower elevation ponds, numbers of nonnatives in the river would rebound <br />periodically: thus progress towards recovery would be less than would <br />occur under alternatives 2 and 3. Nongame nonnative fishes with <br />established riverine populations would continue to be a major problem. <br />2. Recreation: Recreational opportunities in Utah and Wyoming would be <br />unaffected by this alternative. Future private pond owners, below the <br />10-year floodplain, wishing to have fishing would have to purchase trout <br />rather than warmwater fishes from the aquaculture industry. Ponds would <br />probably not be suitable for trout during summer months. Fishing in <br />private ponds would be concentrated during spring and fall months. <br />Warmwater fishing opportunities would continue to increase above the 10- <br />year floodplain. If the same level of warmwater fishing opportunities <br />31