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Last modified
7/14/2009 5:01:47 PM
Creation date
5/20/2009 11:05:23 AM
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UCREFRP
UCREFRP Catalog Number
9484
Author
Osmundson, D. B., V. L. Ryel, V. L. Lamarra and J. Pitlick
Title
Flow-Sediment-Biota Relations
USFW Year
2002
USFW - Doc Type
Implications for River Regulation Effects on Native Fish Abundance
Copyright Material
YES
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1732 D. B. OSMUNDSON ET AL. Ecological Applications <br />Vol. 12, No. 6 <br />160 <br />120 <br />E <br />E <br />CO <br />0 80 <br />FU <br />0 <br />H <br />40 <br />0 <br />2.5 <br />w <br />s 2 <br />0 <br />3 <br />Y <br />0 1.5 <br />rn <br />LL 1 <br />N <br />0.5 <br />0 <br />Year <br />FtG. 6. Mean total (top) and mean relative (bottom) depth-of-free-space (DFS) in run and riffle substrates of stratum 9 <br />(left) and stratum 8 (right) during base flows of 1996-2001. Total DFS is the absolute distance from the top of surface rocks <br />to the level of embeddedness; relative DFS scales absolute distance to the median rock width (measured across the b-axis) <br />at each site. <br />of adult pikeminnow (F, , = 8.0, P = 0.025, r2 = 0.53), <br />an expected result because of the strong relationship <br />between biomass of all fish and riffle area (F,,, = 20.6, <br />P = 0.001, r2 = 0.70). The stronger relationships of <br />adult pikeminnow with numbers and biomass of other <br />fish suggests that food availability is more important <br />than the physical habitat provided by riffles. <br />Given that food availability was most important, the <br />regression for adult pikeminnow densities with biomass <br />of other fish was extended to include area of runs and <br />area of nonriffle/run habitats. This was conducted to <br />assess if the area of other habitats, when combined with <br />food availability (which strongly correlated with rif- <br />fles), further explained the variability in adult pike- <br />minnow densities. This regression was highly signifi- <br />cant (F3,5 = 84.1, P = 0.0001, r2 = 0.98), with all <br />independent factors significant (P G 0.02) and no ev- <br />idence of multicollinearity (condition number = 4.05). <br />When the regression was conducted in a stepwise man- <br />ner, biomass of other fish explained 76% of the vari- <br />ation in density of adult pikeminnow while the other <br />two factors explained 65% of the residual variation, <br />suggesting that habitat heterogeneity and total wetted <br />area (as reflected by the major habitat type, runs) may <br />also influence adult pikeminnow distribution when <br />overlain on food resources. This interpretation of the <br />importance of total wetted area was assessed with a <br />similar stepwise regression using biomass of other fish <br />and total wetted area (F2,6 = 66.3, P = 0.0008, r2 = <br />0.96). Total wetted area explained 65% of the residual <br />variation in density of adult pikeminnow when re- <br />gressed against biomass of other fish. <br />Sediment dynamics <br />Depth of free space.-Total DFS monitored in strata <br />8 and 9 during 1996-2001 showed significant declines <br />in both runs and riffles (Fig. 6) corresponding to de- <br />clines in annual peak flow (Fig. 7). Mean annual total <br />DFS was positively correlated with peak discharge in <br />runs (P = 0.005, r2 = 0.86) and riffles (P = 0.03, r2 <br />= 0.70) of stratum 8 and in runs (P = 0.02, r2 = 0.69) <br />and riffles (P = 0.04, r2 = 0.60) of stratum 9. Declines <br />occurred in both habitat types in both strata in years <br />following 1997, the last year when the thresholds for <br />widespread bed mobilization were exceeded. These de- <br />clines occurred despite thresholds for initial motion <br />having been exceeded in stratum 9 in 1998-2000 and <br />in stratum 8 in 1998. <br />1996 1997 1998 1999 2000 2001 1996 1997 1998 1999 2000 2001
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