LENTIC SESTON ENHANCEMENT OF TAILWATER FISHERIES John S. Sproul 1, Kent A. Hatch 2, Dennis K....
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Transcript of LENTIC SESTON ENHANCEMENT OF TAILWATER FISHERIES John S. Sproul 1, Kent A. Hatch 2, Dennis K....
LENTIC SESTON ENHANCEMENT OF
TAILWATER FISHERIES
John S. Sproul1, Kent A. Hatch2, Dennis K. Shiozawa3
1Biology Program, Brigham Young University, Provo, Utah 84602 USA; 2Long Island University, C.W. Post Campus, Brookville, NY 11548 USA; 3Department of Biology, Brigham Young University, Provo, Utah 84602 USA
What makes tailwater fisheries so productive?
Thermal Hypothesis - High productivity seen in tailwaters may be largely attributed to the thermal effects of the impoundment.
• Impoundments act as temperature buffers to tailwaters• Hypolimnetic releases create cooler summer highs and warmer winter lows in tailwaters
• These buffered temperature conditions provide more degree-days for invertebrate growth and optimal conditions for growth and development of fish
Thermal Hypothesis
Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec0
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Green River prior to FG Dam 1958-1959 (USGS Greendale Gage 09234500)
Green River below FG Dam 2004-2005 (USGS Greendale Gage 09234500)
Thermal Hypothesis
Is temperature the only factor affecting productivity?
• The sources of the energy generating the increase in productivity are not fully defined in the thermal hypothesis. • The emphasis on moderated temperatures alone implies that autochthonous primary production is also enhanced during the extended growing season and that it results in the increased secondary production in the tailwater system. • Yet many investigators have measured significant densities of zooplankton rich reservoir seston in tailwaters.• We attempted to quantify the subsidy of reservoir seston (zooplankton) on tailwater food-webs.
Alloctonous Carbon Source
Autocthonous Carbon Source
Additioinal Allocthonous Carbon Source (animal protein)
*Organisms expanding their diet to include reservoir zooplankton are likely to show an upward shift in trophic position.
Methods
-We collected invertebrates below impoundments of three reservoirs-We compared their stable C and N isotope ratios to invertebrates above the respective reservoirs. -We also analyzed stable isotope ratios in drift, as well as zooplankton netted from the reservoirs.
-We performed MANOVA’s to test for significant differences between sites.
Results
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Hunt A and Hunt B
Hunt A
Hunt B
Results
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Sco A and Sco B
Sco A
Sco B
Carbon
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Straw A and Straw B
Straw A
Straw B
Results
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D. Fork and 6th Water
D. Fork
6th Water
Results
Results
Results
Results
ResultsNitrogen
Location Species Mean Below Mean Above Mean Diff. DF t-Value p-Value
Electric lake Drift 4.106 3.211 0.896 32 -3.157 0.0035
Baetis 7.375 5.808 1.556 23 -11.326 <0.0001
Cynigmula 6.74 5.6548 1.085 9 -4.484 0.0015
Drunella g. 7.709 5.627 2.036 21 -5.705 <0.0001
Rhyacophila 9.314 7.503 1.882 18 -4.208 0.0005
Simuliidae 7.561 5.327 2.234 10 -3.247 0.0088
Strawberry Dam Drift 7.519 3.084 4.435 31 -3.885 0.0005
Baetis 11.226 6.084 5.141 24 -5.646 <0.0001
Epeorus 10.808 5.845 4.963 9 -1.717 0.1201
Simuliidae 10.315 6.005 4.309 17 -3.783 0.0015
Strawberry Tunnel Drift 7.645 1.26 6.385 32 -13.802 <0.0001
Baetis 8.646 6.097 2.549 19 -4.56 0.0002
Brachycentrus 9.974 5.597 4.376 9 -7.205 <0.0001
Drunella g. 11.522 6.334 5.187 10 -9.098 <0.0001
Hydropsyche 11.139 7.322 3.818 18 -10.948 <0.0001
Pteronarcella 9.753 4.816 4.937 12 -6.551 <0.0001
Rhyacophila 11.66 6.938 4.722 12 -4.436 0.0008
Simuliidae 10.74 4.623 6.118 10 -28.999 <0.0001
Scofield Drift 5.25 1.097 3.334 32 -3.48 0.0015
Asellus 7.409 7.679 -0.27 15 0.456 0.655
Leech 10.456 11.09 -0.634 9 0.8 0.4444
Simuliidae 7.56 5.685 1.875 18 -3.37 0.0034
Conclusions
• Lentic seston can provide a significant subsidy to the food base in tailwater food-webs.
-The importance of this subsidy likely varies with factors like reservoir trophy, volume of discharge, etc.
• Future studies could investigate the distance downstream that the isotopic signal of the reservoir persists.
• An understanding of these dynamics can influence management decisions as agencies consider the impact of restoring natural flow/temperature regimes to impounded rivers.
Acknowledgements
-Keith Tanner, Heather Stutz, Michelle Barney, and Chris Hansen for field and laboratory work.
-Funding came from a grant from the Roger and Victoria Sant Educational Endowment for a Sustainable Environment, to Dennis K. Shiozawa.