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<br />-table 1. Initial Missouri River fish and wildlife habitat mitigation sites. in <br />Nebr.15lu. ranked by priority. Acreages shown represent optimum amounts. <br />Development would be possible, however, on smaller acreages without jeopard- <br />izing the benefits derived. Cost includes acquisition in fee-title at 51,000 per acre <br />plus 5100,000 per site t" develop the necessary mitigation. <br /> <br /> Cost <br />Site no. Site name River mile Acreage x $100,000 <br />1 Boyer Chute 638-633 2,600 2.7 <br />2 Goose Island 583-578 1,375 1.5 <br />3 Lower Civil Bend 574-568 2,800 2.9 <br />4 Tobacco Island 589-586 1,560 1.6 <br />5 Honey Creek Complex 541-537 1,690 1.7 <br />6 Van Horn Bend 578-574 8SO 1.0 <br />7 Hamburg Bend 556-552 1,700 1.8 <br />8 Lake Quinnebaugh 686 1,500 1.5 <br /> <br />concert with dike notching should selVe <br />to initiate the erosion necessary to re- <br />cover the old configuration without <br />additional management assistance. <br />Native aquatic vegetation should re- <br />establish as natural hydrologic condi- <br />tions re-develop. Native vegetations <br />should be allowed or assisted to re- <br />establish on terrestrial sites adjacent to <br />the wetlands to simulate the inter- <br />spersion and successional stages that <br />occurred naturally. This habitat would <br />contribute additional organic material <br />and primary energy to the riparian <br />ecosystem, resulting in an expanded <br />food web and enhanced secondary pro- <br />ductivity. Although agricultural pro- <br />duction on the floodplain can reach 9 <br />metric tonnes per hectare per year (tl <br />ha/year) of biomass (Ovington et a1. <br />1963), much of this production is phys- <br />ically removed from the cropped field <br />(floodplain) in the form of grain, forage, <br />or domestic livestock. Native plant <br />communities, which are flooded pe- <br />riodically, can contribute from 6 t/hal <br />year (for grasslands) to 16 t/ha/year <br />(for cattail marshes) of biomass to the <br />ecosystem (Hesse et al. 1986). <br />Water management is an important <br />component of a system-wide plan of <br />mitigation. Temporal flow should co- <br />incide with the natural climatic varia- <br />tion in the basin. Although the up- <br />stream reservoirs should continue to <br />provide necessary flood control, their <br />operation should be adjusted to allow <br />for some higher spring discharges. <br />Present water management criteria typ- <br />ically include storing spring runoff <br />through early summer to prevent in- <br />undation of floodplain cropland. This <br />stored water then is released during <br />late summer and early autumn, often <br /> <br />January - February J989 <br /> <br />inundating the same land protected <br />earlier in the year. This discharge reg- <br />ulation schedule is detrimental to the <br />Missouri River fishery, because most <br />species spawn in spring and early sum- <br />mer in response to high flows. In ad- <br />dition, aquatic insects, which selVe as <br />food sources for these fishes, require <br />high water in the spring for optimum <br />reproduction. In the past, high spring <br />water levels assured that a large num- <br />ber of metamorphosing aquatic insects <br />were present during the summer and <br />autumn to provide a ready food supply <br />for most fish and other vertebrates in <br />the Missouri River ecosystem. Re-es- <br />tablishing the natural timing of high <br />flows, although moderated to allow for <br />flood control needs, could dramatically <br />improve sUlVival of the young-of-the- <br />year fish and is essential to restoring <br />the habitat value of the riparian eco- <br />system as a whole. Research is pres- <br />ently underway that should help to <br />identify the timing and extent of these <br />releases. Change will be acceptable only <br />if we are successful in identifying a <br />regimen satisfactory, in some degree, <br />to all users of the river and its flood- <br />plain. <br /> <br />Funding: How Can It <br /> <br />be Achieved? <br /> <br />A Trust Fund could be established <br />with all or part of the authorized $51.9 <br />million. Additional mitigation needs <br />could be funded through additional <br />congressional appropriations or through <br />an approach patterned after the Pacific <br />Northwest Electric Power Planning and <br />ConselVation Act of 1980 (16 U.S.C., <br /> <br />839 et seq.). This Act created and di- <br />rected the Northwest Power Planning <br />Council (Council) to develop and adopt <br />a ". . . program to protect, mitigate, <br />and enhance fish and wildlife including <br />related spawning grounds and habitat, <br />on the Columbia River and its tribu- <br />taries." The Act further directed that <br />the". . . program, to the greatest extent <br />possible, shall be designed to deal with <br />that river and its tributaries as a sys- <br />tem. " <br />The Council, composed of represen- <br />tatives from the four states in the Co- <br />lumbia River basin, was assigned re- <br />sponsibility for developing a fish and <br />wildlife recovery program. liThe peo- <br />ple of the Northwest, rather than Con- <br />gress and distant federal agencies, are <br />given an opportunity to decide what <br />should be done to protect their fish <br />and wildlife resources and mitigate the <br />hann caused by decades of hydroelec- <br />tric development." The Act also gave <br />the ". . . Bonneville Power Adminis- <br />tration the authority and responsibility <br />to use its legal and financial resources <br />to protect, mitigate and enhance fish <br />and wildlife." The overriding principle <br />was clear: ". . . fish and wildlife inter- <br />ests and power interests shall cooper- <br />ate as partners in the development, <br />operation, and management of the Co- <br />lumbia River hydroelectric system for <br />the benefit of all citizens of the Pacific <br />Northwest." One of the more signifi- <br />cant elements of the Council's fish and <br />wildlife recovery program was a "Water <br />Budget" designed to improve stream- <br />flow and thus enhance migration of <br />Columbia River fishes. <br />The Columbia River mitigation pro- <br />gram prescribed funding sources: in- <br />cluding federal appropriations and <br />power revenue surcharges. The Coun- <br />cil estimated that implementation of <br />their entire program could cost about <br />$700 million over the next 20 years. <br />This would result in increased costs of <br />approximately 0.05 cents per kilowatt <br />hour of energy sold by Bonneville Power <br />Administration (Northwest Power <br />Planning Council 1982). <br />The electrical generating capacity of <br />the Federal Columbia River Power Sys- <br />tem was 13,000 megawatts in 1975. By <br />comparison, the Pick-Sloan Missouri <br />Basin Project hydroelectric plants have <br />a current capacity of 3,000 megawatts. <br />This power is marketed by the Western <br />Area Power Administration (WAPA) <br />and the Southwest Power Administra- <br /> <br />13 <br /> <br /> <br />