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in Colorado are to be maintained. Colorado and the Recovery Program <br />would have to seek opportunities elsewhere. including ponds above the <br />10-year floodplain. This might include agreements with entities such as <br />water districts that own waters not currently available to the public <br />for fishing. Colorado would likely berm some public waters to FEMA <br />standards to maintain fishing. Because warmwater fishing in Colorado <br />represents a small percentage of the total fishing, overall numbers of <br />fishing days are unlikely to decrease significantly. <br />3. Recovery of Endangered Fishes: The few ponds that might be bermed to <br />FEMA standards would reduce and isolate the amount of floodplain habitat <br />available to the endangered fishes during high flow events. Nutrients <br />and plankton in these floodplain habitats will be isolated from the <br />river. Ponds bermed to FEMA standards may also have positive benefits <br />including: 1) preclude re-invasion of the river by nonnative sport fish <br />stocked into that pond, 2) would not trap endangered fishes during high <br />flow events, and 3) preserve warmwater angling opportunities in some <br />ponds. Flogs greater than a 10-year event will still allow nonnative <br />fishes to escape to the river and establish in lower elevation ponds <br />that are reclaimed though Recovery Program efforts. Recovery would <br />continue to be impacted by nonnative fishes in the system. <br />4. Economy: Costs of berming ponds to FEMA standards could be <br />significant. It is likely that stocking of private ponds with warmwater <br />species would decrease causing impacts to the warmwater fish brokers in <br />the aquaculture industry. This may be partially offset by increased <br />trout purchases by the private sector. The change in overall fishing <br />days in 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 />F. Alternative 5. <br />1. Aquatic Biological Resources: Stocking in the floodplain (above the <br />10-year floodplain) would continue and some escapement would continue to <br />occur. Any increases in the numbers of ponds with warmwater sport fish <br />above the 10-year floodplain would be offset by decreases in the number <br />of ponds below the 10-year floodplain. Stocking above the 10-year <br />floodplain would allow for the periodic escapement of nonnative fish <br />into the river. These same fish would serve as seed fish for ponds that <br />had been reclaimed, thereby compounding pond reclamation efforts. <br />Because of the problem of fish above the 10-year floodplain and upstream <br />of critical habitat reseeding lower elevation ponds, numbers of <br />nonnatives in the river would rebound periodically. Nongame nonnative <br />fishes with established riverine populations would continue to be a <br />major problem. <br />2. Recreation: Recreational opportunities in Utah and Wyoming would be <br />unaffected by this alternative. Future private ponds below the 10-year <br />32