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<br />for instance, holds that the deple- <br />tion of water anywhere in the Up- <br />per Colorado River Basin will ad- <br />versely affect the four endangered <br />, fish species that reside in the <br />lower, warm-water reaches of the <br />Upper Basin rivers. As a conse- <br />quence, depletion activities far <br />upstream of the habitat are con- <br />sidered to "jeopardize" the endan- <br />gered species, even though endan- <br />gered species habitat may be hun- <br />dreds of miles downstream. <br />The application of the act has <br />been expanded, and it now encom- <br />passes grazing permits issued by <br />federal agencies to individual <br />ranchers, federally funded conser- <br />vation activities on farms, and <br />practically all activities on lands <br />managed by any federal agencies, <br />including the Bureau of Land Man- <br />agement, the U.S. Forest 'Service, <br />and the Department of Defense. <br />The act is applied to contracts be- <br />tween the Bureau of Reclamation <br />and individual water users that <br />address water from federal projects, <br />the annual operation of federal <br />water and power projects, and hy- <br />droelectric power generation op- <br />erations that change the flows in <br />rivers and streams. Moreover, per- <br />mits issued by the Federal Energy <br />Regulatory Commission are sub- <br />ject to Endangered Species Act <br />compliance. Almost any project to <br />benefit American Indians on their <br />own reservations is also subject to <br />Endangered Species Act compli- <br />ance and restrictions, since these <br />are all normally a function of some <br />federal activity. The vast federal <br />land ownership in the western <br />states also triggers application of <br />the Endangered Species Act to <br />countless activities. <br />Clearly, the Endangered Species <br />Act can affect water users through- <br />out the western United States, <br /> <br />001011 <br /> <br />ranging from the individual <br />farmer, rancher, or irrigator to the <br />largest municipalities and indus- <br />tries. Water development activities <br />by American Indians are equally <br />subject to the provisions of the <br />Endangered Species Act. <br /> <br />Economics and the Act <br />The Endangered Species Act, as <br />written and in practice, is virtu- <br />ally devoid of economic consider- <br />ations. In this way it is unique in <br />American law. Listing of species as <br />threatened or endangered requires <br />no consideration of the resultant <br />economic impacts. The Fish and <br />Wildlife Service has routinely con- <br />cluded that listing a species is not <br />subject to provision of the Na- <br />tional Environmental Policy Act, <br />a federal act designed to disclose <br />the impacts of federal actions on <br />the human environmen~. As a re- <br />sult, there is no economic or envi- <br />ronmental review of the impacts <br />of listing endangered species. <br />Critical habitat designation is <br />subject co economic impact analy- <br />sis, but these economic analyses <br />routinely conclude that critical <br />habitat designation does not have <br />a significant economic impact in <br />itself or that the impact is mini- <br />mal on a national or regional scale. <br />Thus, the federal government <br />evades any substantive analysis of <br />economic or environmental im- <br />pacts for implementing the act. <br />This lax approach co economic <br />analysis occurs despite the drastic <br />impacts of the act in some areas <br />and on some economic sectors. For <br />significant examples in the Pacific <br />Northwest, you need look no fur- <br />ther than the spotted owl and sev- <br />eral species of endangered salmon. <br />In fiscal year 1997, reponed fed- <br />eral and state expenditures for the <br />three species of Columbia Basin <br /> <br />salmon totaled $72.2 million.4 <br />Expenditures for these species <br />have occurred in the past and will <br />continue into the foreseeable fu- <br />ture. The economic effects on the <br />timber industry and associated <br />communities and on hydroelectric <br />power production and costs are <br />significant. <br />There was a previous agreement <br />that the Bonneville Power Author- <br />ity (BPA), which generates hydro- <br />electric power in the Pacific North- <br />west, would expend no more than <br />$435 million per year, on average, <br />on endangered species and other <br />fish and wildlife purposes. These <br />costs are passed on to BPA power <br />customers. Of this total $183 mil- <br />lion would result from lost rev- <br />enues from power generation in <br />order to meet flow requirements <br />for fish, and co purchase power <br />resulting from lost generation ca- <br />pacity. BPA is now operating un- <br />der a biological opinion recently <br />issued by the National Marine <br />Fisheries Service. BPA estimates it <br />may have to spend as much as $2.0 <br />billion to purchase power in 2001, <br />while operating under the biologi- <br />cal opinion issued by National <br />Marine Fisheries Service.5 <br />Federal regulations to imple- <br />ment Section 7, "Interagency Co- <br />operation," state that "reasonable <br />and prudent alternatives" must be <br />"economically and technologically <br />feasible." Reasonable and prudent <br />alternatives are alternative actions <br />that can be implemented to avoid <br />the likelihood of jeopardizing the <br />listed species or the destruction or <br />adverse modification of critical <br />habitat. In other words, reasonable <br />and prudent alternatives are miti- <br />gation measures for impacts on en- <br />dangered species, resulting from <br />actions of federal agencies. <br />The determination of what is <br /> <br />Spring 2001 . 47 <br />