Assessment of Stonefly Abundance and Body-Length Based on Rainbow Trout Population in Burch Creek, Ogden Utah, J Abbott, S Green, C Hoagstrom, B Galbraith, J Green

Tags: rainbow trout, Burch Creek, stoneflies, Surber Sampler, Perlidae, Brady Radmall, native cutthroat trout, Perlodidae, J. T. Peterson, Ogden, Utah Fall, Electrofishing, Chloroperlidae, Southwestern Naturalist, Insect Order Plecoptera, F. Pezold, Introgressive hybridization, Christopher Hoagstrom, Wasatch Mountains, Utah, Ogden Utah, Ogden River, northern Utah, Ogden Utah James Abbott, Seth Green, Weber State University, Bryce Galbraith, Ogden, Utah Introduction Rainbow trout, Jeremy Green, Ogden, Utah
Content: Assessment of Stonefly Abundance and Body-Length Based on Rainbow trout Population in Burch Creek, Ogden Utah
James Abbott, Seth Green, Christopher Hoagstrom, Bryce Galbraith, Jeremy Green, Christopher McFarland, Brady Radmall, Thomas Smith Department of Zoology, Weber State University, Ogden, Utah
Introduction Rainbow trout (Oncorhynchus mykiss) are one of the most widely introduced species in the western United States and are often used to promote sport fishing (Weigel, et al. 2003). A primary food source for rainbow trout is stoneflies (Insect Order Plecoptera); representing over 30% of trout diets where populations permit (Metcalf, et al. 1997). Both trout and stoneflies are present in Burch Creek, near Ogden, Utah. It is likely these two species interact in a variety of ways. Feltmate and Williams (1989) found that not only is stonefly density affected by rainbow trout predation, but stoneflies may also evacuate certain habitats to avoid the perceived threat of trout predation. While stoneflies of some families are a food source for rainbow trout, others may compete with trout in places where their shared insect prey are scarce. For example, large stoneflies of the family perlidae appear to compete with rainbow trout for prey, whereas smaller perlodid stoneflies do not (Harvey 1993). In order to better understand how stoneflies interact with trout, we compared trout abundance with abundance and size of stoneflies from three different families: Chloroperlidae, Perlidae, and Perlodidae (Figure 1). Study Objective Compare the results of our study with the findings from Harvey's (1993) study of local creeks along the Wasatch Front. He found that the perlodid stonefly numbers increased in the presence of trout, whereas perlid stoneflies decreased. He also found that perlid stoneflies increased in length in the absence of trout. We wanted to see if the abundance and size of stoneflies were affected by the presence of trout.
Methods and Analyses Burch Creek is located in the Wasatch Mountains of northern Utah and flows west through Burch Creek Canyon toward the city of Ogden, Utah (Figure 2). As the stream arrives at the eastern edge of Ogden City limits it discharges into a concrete canal and the confined water continues westward to the Weber River. Before entering the canal, the stream passes through a metal grate that limits the fauna that can proceed to the lower reaches. Above the grate the stream is characterized by low flow rates, a high gradient, and a relatively rocky substrate. The canyon flora is composed primarily of birch, willow and aspen. Burch Creek supports a sizeable community of non-native rainbow trout, as well as a wide variety of invertebrates.
0 0.5 1
2
3
4
Kilometers
Goode Ski Lake Lorrin Farr Park
Oaks Restaurant Indian Trailhead
Wall Avenue
Dinosaur Park
Legend = Ogden River = Pineview Reservoir = Electrofishing survey location
Figure 1. Map of six study reaches in the Ogden River, Utah during 2009.
Figure 2. Map of Burch Creek, Ogden Utah and selected sample sites We estimated rainbow trout abundance and stonefly size and abundance in four sites along Burch Creek during fall 2010. Site elevations were 1570 m, 1660 m, 1775 m, and 1850 m. We collected trout with a backpack electrofisher (Figure 6) and measured the length of each trout to the nearest millimeter. We collected stoneflies in 10 evenly spaced locations along the creek using a 1-ft2 Surber sampler (Figure 3). Stoneflies were identified to family and stonefly length (excluding cerci) was measured to the nearest 0.1 mm with calipers. We compared abundance of rainbow trout to the abundance and length of stonefly families.
Results
20
Average Number of Stoneflies
15
10
5
0 0
8
44
54
Number of Trout
Figure 4. Comparison of rainbow trout abundance among sites and stonefly abundance within families Chloroperlidae (purple), Perlodidae (green), and Perlidae (blue).
The abundance and size of stoneflies within each of the three families was relatively consistent regardless of the abundance of trout (Figures 4 and 5). Stoneflies of family Chloroperlidae were most abundant and perlid stoneflies were least. Chloroperlid and perlodid stoneflies were relatively small, whereas perlid stoneflies were more variable in size but included very large individuals.
25
Average Stonefly Length (cm)
20 15
10 5
0
0
8
44
54
Number of Trout
Figure 5. Comparison of rainbow trout abundance and stonefly body length within families Chloroperlidae (purple), Perlodidae (green), and Perlidae (blue).
Discussion Our study showed populations of the stonefly family Perlodidae were lowest at the site having the highest density of rainbow trout, which contradicted Harvey's (1993) findings. Also, the average body size of perlodid stoneflies was similar among sites, regardless of trout abundance. Perlidae also showed no general trends relative to the abundance of trout, being rare at all sites, perhaps due to competition with trout. However, their rarity at locations with few or no trout suggests habitat was unsuitable. Highly variable average size of perlid stoneflies among sites was due to the small number of individuals at each site. Harvey (1993) did not study stoneflies of family Chloroperlidae, but in our study, they were the most abundant. Chloroperlid numbers decreased in the presence of trout, with the exception the site with the most trout. However, exceptionally high abundance at this site was due to a single sample from a shallow habitat that was likely a refuge from trout. As with perlodid stoneflies, chloroperlid stoneflies were similar in average size regardless of trout abundance. In summary, we could neither fully support nor contradict Harvey's (1993) findings. Rainbow trout did appear to influence abundance of smaller stoneflies, which suggests Harvey's findings do not hold in all streams along the Wasatch Front. Abundance of chloroperlid stoneflies in our study and rarity of perlid stoneflies could reflect habitat differences between Burch Creek and the creeks Harvey sampled or could indicate that stonefly distributions have changed over time. More widespread sampling within Burch Creek and within creeks studied by Harvey might provide better resolution on relations among stoneflies and rainbow trout.
Figure 1. Images of Chloroperlidae, Perlidae, and Perlodidae from top to bottom respectively. Photos courtesy of Troutnet.com nwnature.net 02/10/2011
. Figure 3. Collecting invertebrates using a Surber Sampler. Photo courtesy of Also.org 02/10/2011
Figure 6. Electrofishing on Burch Creek, Ogden, Utah Fall of 2010.
Literature cited Weigel, D. E., J. T. Peterson, and P. Spruell (2003) Introgressive hybridization between native cutthroat trout and introduced rainbow trout. Ecological Applications 13: 38-50. Metcalf, C., F. Pezold, B. G. Crump (1997) Food Habits of introduced rainbow trout (Oncorhynchus mykiss) in the upper Little Missouri River drainage of Arkansas. The Southwestern Naturalist 42: 148-154 Harvey, B. C., (1993) Benthic assemblages in Utah headwater streams with and without trout. Canadian Journal of Zoology 71: 896900. Feltmate, B. W., D. D. Williams (1989) Influence of Rainbow Trout (Oncorhyncus mykiss) on Density and Feeding behavior of a Perlid Stonefly. Canada Journal of Fisheries Aquatics 46: 1575-1580.

J Abbott, S Green, C Hoagstrom, B Galbraith, J Green

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