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Last modified
1/26/2010 12:29:33 PM
Creation date
10/11/2006 10:13:12 PM
Metadata
Fields
Template:
Water Supply Protection
File Number
8062
Description
Federal Reserved Water Rights
State
CO
Basin
Statewide
Date
3/1/1995
Author
USDOC
Title
Instream Flow Incremental Methodology - A Primer for IFIM
Water Supply Pro - Doc Type
Report/Study
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<br />O.-?'3 <br />" IJJwl <br /> <br />OulpUI 01 Microhabitat Model <br />(reaell specilic, Iile stage specific) <br /> <br />E <br />'" <br />e <br />~v; <br />fj'O <br />LC LC <br />~o. <br />~ ~ Life stage specIfiC <br />~- <br />::>:g <br />~ <br />Q; <br />a. <br /> <br /> <br />Flow (dsl <br /> <br />Fig. 2.2. Flo\'....habitat relation developed by uSing <br />PHABSIM. <br /> <br />'1 <br /> <br />versus now function showing how incremental <br />changes in flow result in quantifiable changes in <br />habitat value, <br />Even the best mid-range techniques leave the <br />analyst open to criticism, There are two fre- <br />quently challenged features ofPHABSIM, First is <br />the necessity for species suitability criteria (esti- <br />mated species responses to stream variables. nor- <br />malized onto a response cun'e), Figure 2.3 depicts <br />e%ample suitability criteria for two life stages of <br />brown trout, The curves show' that adults use <br />deeper and faster water than do juveniles. These <br />criteria may be established by several methods <br />ranging from solicitation of expert opinion to site- <br />specific collection and verification of field data <br />(Bovee 1986; Modde and Hardy 1992, (Thomas <br />and Bovee 1993), All of the criteria development <br />methods have been challenged to some degree, <br /> <br />.~ <br /> <br />-, <br />) <br />., <br />., <br /> <br />Brown Troul (Adult) <br /> <br />.. <br /> <br />it'OC'O <br />.~ D.!l 05 <br />, <br />'" <br />0.0 <br />o 5 10 <br /> <br />, <br /> <br />,. <br />" <br /> <br /> <br />Brown Trout (Juvenile) <br /> <br />.~ <br />, <br />.. <br /> <br />f ::~ ::~ <br />00 OO~ <br /> <br />o !l \0 0 5 10 <br /> <br />Deplh(tt.) <br /> <br />Velociry (Ips) <br /> <br />f <br />1 <br /> <br /> <br /> <br />0' <br /> <br />\0 <br /> <br />'0 <br /> <br />0' <br /> <br />THE INSTRt=;AM fLow INCREMEl\'TAL METHOLOOlOGY 13 <br /> <br />The second criticism concerns the requirement to <br />analyze habitat species by species. which may not <br />account for habitat selection a!Tected by interspe- <br />cies competition (Ross 1986; Hearn 1987; Modde <br />et al. 19911. Note that the quality of habitat suit- <br />ability data, along with the signIficance of PHAB- <br />SIM's driving variables (e.g., depth, velocity, sub- <br />strate material, and cover), forms the basis for <br />most criticisms of this technique (Morhardt 19861, <br />To satisfy such criticisms, more in-depth analysis <br />is needed than is usually undertaken in simple <br />PHABSIM or HQI studies, PHABSIM is an incre, <br />mental method in the sense that it predicts <br />changes in habitat resulting from changes in flow, <br />but it focuses on onl)' a few variables affecting <br />localized fish behavior and ignores the dynamics <br />of habitat through time, The use of PHABSIM <br />alone also ignores many other biotic factors such <br />as inter- and intra-specific interactions. <br /> <br />Incremental Techniques <br /> <br />The mid-range techniques essentially provide <br />temporal snapshots of stream resources, When the <br />imperatives of negotiation or court proceedings re- <br />quire a more d)'namic look at the instream now <br />question, other techniques are needed. These pro. <br />ject bargaining problems have been labeled 'incre- <br />mental' <Trihey and Stalnaker 1985) because a <br />deep knowledge of how aquatic habitat value <br />changes as a functiOn of incremental changes in <br />streamt1.ow is required, This detailed quantifica- <br />tion must be developed to prepare for negotiations <br /> <br />. <br /> <br />" <br /> <br />Fig. 2.3. Suitabilily-of-use Curves for <br />bro.....n trout. <br /> <br />. <br />Channel index <br /> <br />12 <br />
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