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Last modified
7/14/2009 5:02:31 PM
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5/22/2009 6:51:58 PM
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UCREFRP
UCREFRP Catalog Number
7859
Author
United States Congress, O. o. T. A.
Title
Fish Passage Technologies, Protection at Hydropower Facilities.
USFW Year
1995.
USFW - Doc Type
Washington, D.C.
Copyright Material
NO
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4 ~ Fish Passage Technologies: Protection at Hydropower Facilities <br />This controversy over whether riverine fish <br />need safe passage relates to whether or not <br />movement to habitats blocked by a dam have <br />adverse impacts on the population. Although the <br />paradigm is beginning to change, the predomi- <br />nant thinking has been that riverine fishes have <br />restricted movements. This may be true at some <br />sites, but the generalization may in part be an <br />artifact of the movement studies that have been <br />done. Recent research has identified major dif- <br />ferences in fish movements among different spe- <br />cies of riverine fish and there are some studies <br />that document different movements of the same <br />species in different watersheds. The need for mit- <br />igation to provide passage for riverine fishes is <br />most likely site- and species-specific and should <br />be tied to the specific habitat needs for target fish <br />populations in a given river reach. <br />Tho controversy over whether riverine fish <br />need protection from entrainment is lazgely unre- <br />lated tlo issues about passage requirements (see <br />chapter 2). The controversy centers on the lack of <br />information on the impact of entrainment on the <br />overall fish population. Population impact stud- <br />ies would be exceedingly complex, time consum- <br />ing anti costly, and are rarely, if ever, done (146). <br />The hydropower industry and resource agencies <br />take vjery different positions about the need for <br />entrainment protection, given the lack of good <br />site-specific information. Industry generally says <br />that entrainment protection is not necessazy for <br />riverine fish. Resource agencies consider entrain- <br />ment achronic loss of fish that requires mitiga- <br />tion, or at least compensation. As a result of this <br />controversy, entrainment and turbine mortality <br />studied are frequently done. These studies also <br />have limitations. <br />Tho National Marine Fisheries Service <br />(NMFS) and the U.S. Fish and Wildlife Service <br />(FWS), referred to throughout this report as fed- <br />eral resource agencies, have the authority to pre- <br />scribe it mandatory fish passage mitigation under <br />section 18 of the Federal Power Act, as amended <br />(FPA),~ These agencies, along with their state <br />counterparts, may also make additional recom- <br />mendations to protect, mitigate, and enhance fish <br />and wildlife affected by hydropower develop- <br />ment under section 10(j) of the FPA. The deci- <br />sion to include section 10(j) recommendations in <br />a hydropower license order rests with the Federal <br />Energy Regulatory Commission. FERC is <br />required to balance developmental and nondevel- <br />opmental values of hydropower development in <br />the licensing process. This requires an evaluation <br />of the need for (i.e., benefits) and costs of recom- <br />mended mitigation compared to the benefits of <br />the hydropower project; such evaluations have <br />many limitations. <br />Apart from the controversies about the need <br />for fish passage and protection, there are issues <br />about the technologies (boxes 1-3 and 1-4). For <br />upstream technologies, the issues relate to proper <br />design, operation and maintenance,- understand- <br />ing fish behavior, and the need to develop tech- <br />nologies for additional species (see chapter 3). <br />These upstream technology issues are not partic- <br />ularlycontroversial. <br />For downstream technologies, the primary <br />controversy is the value of investing time and <br />money in alternative behavioral technologies, <br />especially for conditions where conventional <br />methods with high levels of effectiveness are <br />possible. This issue is highly controversial and <br />complex (see chapter 4). It is not readily <br />explained without an understanding of the tech- <br />nologies for fish passage and the different posi- <br />tions of key stakeholders, including: <br />^ resource agencies with responsibilities for pro- <br />tection of fish species, many of which aze in <br />serious decline; <br />^ hydropower operators with the mission of pro- <br />viding arenewable form of electricity without <br />the emissions and adverse environmental <br />effects associated with alternative generation <br />methods; many operators aze seriously con- <br />cerned about their viability in anticipated <br />deregulated markets; and <br />^ developers of new technologies who are con- <br />vinced they have viable approaches to fish <br />passage and protection that will cost much less <br />than conventional methods. <br />Resource agencies take the position that con- <br />ventional downstream passage technologies <br />should be installed because the al±ernative meth- <br />
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