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Study Plan - Biological Resource Responses to Fall Steady Experimental Flows Feruary 2010
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Study Plan - Biological Resource Responses to Fall Steady Experimental Flows Feruary 2010
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Last modified
7/25/2012 4:16:53 PM
Creation date
7/25/2012 2:23:31 PM
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Water Supply Protection
Description
Study Plan - Biological Resource Responses to Fall Steady Experimental Flows released for Glen Canyon Dam 2009-12
State
CO
Date
2/1/2010
Title
Study Plan - Biological Resource Responses to Fall Steady Experimental Flows
Water Supply Pro - Doc Type
Report/Study
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a b <br />25 - _ . - _ - 25 <br />t df =1 I L (it =2 <br />F -value = 87 79 F -value = T60 b <br />�C 20 p <0.001 "c 20 P = 0.009 b <br />O O <br />rn rn <br />15 15 <br />0 a <br />T_, <br />0 10 T - 0 10 <br />O 0 i <br />_ 3 E s <br />-0 5 -0 5 j <br />O - -�: -0 <br />t z <br />0 - 0 <br />10 15 STABLE LFV HFV <br />Water Temperature ('C) Flow Treatment <br />Figure 1. The effect of water temperature (a) and flow treatments (b) on net production. <br />LFV = Low Fluctuating Velocity and HFV = High Fluctuating Velocity. Different letters <br />above bars in panel b denote significant differences among treatment levels based on <br />Tukey's HSD test. Data are preliminary and have not been peer- reviewed. <br />a b <br />0.14 - - - 0.14 ...... <br />d1 =1 _ ilf =2 <br />0.12 - F -value = 17.05 = 0.12 - F -value = 2.98 <br />> _ > P =0089 I <br />CO p =0.001 <br />0 10 - Q. -. - 3.2 -` r 70 0 10 . <br />N N <br />0.08 0.08 i e <br />0 0 0 -06 <br />0.06`' <br />'O O.04 0.04 - <br />0.02 002 - <br />t = <br />000 - - - ---- 0.00 - - <br />10 15 STBL LFV HFV <br />Temperature ( "C) Flow Treatment <br />Figure 2. The effect of Water Temperature (a) and Flow Treatments (b) on the Individual <br />Growth Rates of black fly larvae. LFV = Low Fluctuating Velocity and HFV = High <br />Fluctuating Velocity. Black flies were left in streams for 10 days. Data are preliminary <br />and have not been peer- reviewed. <br />Accumulation of algae and invertebrate biomass might be higher during steady flows if rates of <br />sloughing and downstream export are higher when discharge is fluctuating. However, rainbow trout and <br />humpback chub have been documented to forage on drifting food items (Valdez and Ryel, 1995; <br />McKinney and Speas, 2001), so increases in benthic biomass because of a decrease in sloughing may <br />actually reduce the quantity of drifting food items that are available to these species. Benthic biomass <br />data are inherently variable (Stevens and others, 1997) and it seems unlikely that 2 months of steady <br />flows in the fall, a time when primary production is decreasing and steady -flow mediated increases in <br />nearshore warming are likely minimal (Korman and others, 2006), will lead to a detectable <br />8 <br />
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