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7/14/2009 5:02:30 PM
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UCREFRP
UCREFRP Catalog Number
7405
Author
Bain, M. B., ed. 1990.
Title
Workshop Synopsis,
USFW Year
Ecolog
USFW - Doc Type
U.S. Department of the Interior,
Copyright Material
NO
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<br />26 BIOLOGICAL REPORT 90(5) <br /> <br />The IBI: A Quantitative, Easily Communicated Assessment of <br />the Health and Complexity of Entire Fish Communities1 <br /> <br />by <br /> <br />Robert M. Hughes <br /> <br />U.S. Environmental Protection Agency <br />Environmental Research Laboratory <br />NSI Technology Services Corporation <br />200 SW 35th Street <br />Corvallis, Oregon 97333 <br /> <br />Two basic questions face biologists interested in <br />assessing and predicting impacts on stream ecosys- <br />tems: Why do we need assessments of biological <br />communities? How can data on biological commu- <br />nities (species and abundances) be made useful for <br />nonbiologists (decision-makers and the public)? <br />Answers to these questions are central to im- <br />plementing the Clean Water Act. Although the act <br />requires restoration and maintenance of biological <br />integrity (Section 101) and biological assessment <br />(Sections 105, 303, 304, 305, 404), biological integ- <br />rity remains poorly defined and rarely measured. <br />States are required to establish water quality stan- <br />dards consisting of designated biological uses (broad <br />goals) and criteria (which if met are presumed to pro- <br />tect the uses); however, both the uses and the na- <br />tional chemical criteria are inaccurate. Uses such as <br />aquatic life and warmwater fish are so broad as to <br />be met by any form of aquatic life or species of fish, <br />in any abundance. <br />Nationally established chemical criteria ignore <br />naturally occurring differences in conventional <br />water quality parameters, such as dissolved oxygen, <br />pH, and the ionic character of waters. The ionic <br />character of waters is particularly important <br />because it affects the activity of toxic chemicals. <br />Equally important, single-chemical criteria do not <br />consider combined-chemical effects, which may <br />mitigate or magnify results. Single-species toxicity <br />tests may not be appropriate or sensitive measures <br />of ecosystem effects because test species may not <br /> <br />IThis paper was funded by the U.S. Environmental Protection <br />Agency through Contract 68-C8-0006 to NSI Technology <br />Services Corporation. It has been subjected to EP A's peer and <br />administrative review and approved for publication. An earlier <br />draft benefited from reviews by M. Bain, J. Kurtenbach, <br />1. Schlosser, and D. Vanna-Miller. <br /> <br />be representative of indigenous species or the most <br />sensitive species and because populations can be <br />devastated by indirect effects on competitors, <br />predators, and prey. Furthermore, criteria exist for <br />only a small number of chemicals. It is too expen- <br />sive to develop specific criteria for every site, and <br />it would create immense regulatory problems if they <br />were developed. Water quality monitoring data are <br />difficult to interpret because of the lack of an ap- <br />propriate sampling and reporting framework and <br />because of the weak link between water quality and <br />ecosystem structure and function. Finally, there are <br />many other factors besides toxics that may limit at- <br />tainment of biological integrity. <br />Like toxics, physical habitat conditions are also <br />surrogate measures of the communities that agen- <br />cies are mandated to protect. Although physical and <br />chemical conditions are necessary for understanding <br />and explaining biological conditions, biological <br />monitoring is preferable in many cases because it <br />provides a direct assessment of the biological com- <br />munity. Moreover, the biota reflect the integrated <br />chemical and physical quality of an area, and they <br />often can be assessed at lower cost than physico- <br />chemical habitat parameters, such as priority <br />pollutants and species-specific habitat. Millions of <br />dollars have been spent on chemical monitoring and <br />on the development of in stream flow models; still, <br />there is only limited quantitative information regard- <br />ing the health of the resident biota at those sites. <br />In the southeastern United States (unlike the West, <br />where the methodology developed), meeting in- <br />stream flow requirements for game fish or a small <br />number of nongame species is underprotective of the <br />entire fish assemblage because (I) most game species <br />have wider habitat-flow tolerances (e.g., centrar- <br />chids vs. salmonids), (2) many nongame species have <br />narrower habitat tolerances than the game species, <br /> <br />~ <br />
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