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NONNATIVE FISH PREDATION THREAT 1947 <br />Taat.E 2.-River temperature (°C) and per-capita consumption (g) by smallmouth bass, northern pike, and channel catfish in <br />the Yampa River, Colorado, over four seasonal time periods. Two simulations were performed: (1) realized piscivory (RP) based <br />on diet data from 2003-2005 and (2) potential piscivory (PP) based on diet observations when small-bodied fishes were <br />abundant (see Methods). The PP scenario for channel catfish is not presented, because diet did not differ from that measured <br />during the late 1980s (Tyus and Nikirk 1990). <br /> smallmouth bass Northem pike Channel catfish <br />Time Mean Crayfish, Fish Fish Crayfish, Fish Fish Crayfish, Plant matter Fish <br />period temperature insects (RP) (RP) (PP) insects (RP) (RP) (PP) insects (RP) (RP) (RP) <br />Jarr-Maz 0.8 18.0 1.2 12.8 63.0 163.7 205.3 23.0 13.0 0.1 <br />Apr-Jun 11.9 259.6 16.6 183.8 288.3 748.8 939.5 354.0 199.7 1.1 <br />Ju]-Sep 19.8 578.8 36.9 409.7 577.0 1,498.5 1,880.3 653.2 368.6 2.0 <br />Oct-Dec 3.9 35.9 2.3 25.4 115.8 300.8 377.4 37.4 21.1 0.1 <br />Annual 9.2 892.4 57.0 631.7 1,044.1 2,711.7 3,402.5 1,067.6 602.4 3.3 <br />potential piscivory by the smallmouth bass and <br />northern pike populations was about 186 <br />kg• km-1 • year], and total consumptive demand (of <br />all food types) by these two populations was 269 <br />kg• km-t • years. The majority (55-67%) of each <br />predator's annual consumption occurred during July- <br />September (Table 2), when water temperatures were <br />closest to the thermal optima of these species. <br />The potential number of age-1 prey (i.e., SBFs) <br />consumed by smallmouth bass ranged from 23,500 to <br />470,000 fish•km-1•year 1 (3,800-75,800 fish- <br />ha t • year 1), depending on prey species. This amount <br />was approximately an order of magnitude higher than <br />SBF consumption by northern pike (Table 3) and was <br />proportional to the difference in biomass consumed by <br />the two species. Because of their relatively small <br />weights at age 1, the potential number of roundtail <br />chub, speckled dace, and mottled sculpin consumed <br />was about 2-20 times higher than that of the remaining <br />five species (Table 3). If smallmouth bass consumed <br />fish of a size equal to the median prey :predator length <br />ratio calculated from gut analyses, then the number <br />consumed would range from 93,600 bluehead <br />suckers • km-1 • year 1 (15,100 fish • ha 1 • year 1) to <br />301,000 speckled dace•km-1•year l (48,500 fish- <br />ha 1 • year l). Alternatively, if smallmouth bass con- <br />sumed the same biomass of fish but at sizes near the p5 <br />of the prey :predator length ratio, then the number of <br />fish consumed would be about sevenfold higher. <br />Northem pike chose to consume much larger individ- <br />uals and thus a lower number of prey (700-1,300 <br />fish • km 1 • year t or 113-210 fish • ha 1 • year] ). <br />Growth trajectories of prey indicated that speckled <br />dace and mottled sculpin do not ultimately grow large <br />enough to exceed the smallmouth bass gape limit, but <br />the other six species outgrow that size at some point <br />between ages 1 and 2. Only Colorado pikeminnow and <br />flannelmouth suckers reach a body size greater than the <br />gape limit of the average northern pike; this occurs at a <br />point between ages 3 and 4. <br />Discussion <br />Bioenergetics model simulations allowed us to (1) <br />provide quantitative evidence that nonnative fish <br />predation was probably having a significant impact <br />on native fish populations of the Yampa River and (2) <br />Taet,e 3.-Potential annual consumption of small-bodied native fishes by smallmouth bass and northern pike populations in <br />the Yampa River, Colorado, 2003-2005. Small-bodied fish equivalents (SBFs) were computed from annual biomass consumed <br />by each predator population and (1) the mean weight of each prey species at age 1 (see Methods) or (2) the median (and 5th and <br />95th percentiles) of the prey :predator size ratio (total length [TL], mm) estimated from predator stomach contents. Blank cells <br />indicate that the size computed from the prey :predator ratio was not attained by that prey species. <br /> <br />Prey species Prey size at age 1 <br />TL (mm) Weight (g) smallmouth bass SBFs (103 prey/km) <br />Age 1 Size thresholds Northem p <br />Age 1 ike SBFs (103 prey/km) <br />Size thresholds <br />Bluehead sucker 81 7.2 23.5 93.6 (15.2-626) 2.4 0.7 (0.1-4.1) <br />Colorado pikeminnow 71 2.3 72.0 207 (29.9-1,566) 7.3 1.3 (0.1-8.7) <br />Plannelmouth sucker 73 2.8 59.2 183 (26.4-1,384) 6.0 1.2 (0.1-7.7) <br />Humpback chub 76 3.5 47.8 168 (24.8-1,246) 4.9 1.1 (0.1-7.1) <br />Razorback sucker 78 5.8 29.0 106 (t6.7-731) 3.0 0.8 (0.1-4.6) <br />Roundtail chub 55 1.3 127 164 (24.2-1,203) 12.9 1.1 (0.1-6.9) <br />Speckled dace 69 1.4 117 301 (45.Z-2,160) 11.9 (12.9) <br />Mottled sculpin 32 0.4 470 110 (5.6-852) 47.9 (4.6) <br />