Catch per Unit Effort as an Indicator of Fish Abundance in Lewis Lake, Yellowstone National Park, Wyoming

Author

Matthew D. Shaughnessy

Objectives

  • Estimate species abundance

  • Calculate catch for target species

  • Calculate mean length for target species

  • Calculate Catch per unit effort (C/f) for target species

  • Visualize spatial distribution of C/f across four distinct quadrants within Lewis Lake

  • Hypothesize areas of ecological significance to Lake Trout

Background

Lewis Lake is located within the Snake River drainage at the headwaters of the Lewis River in Yellowstone National Park (YNP). It is the third-largest body of water in YNP, with a maximum depth of 32.9 m and a surface area of approximately 1,099 ha. The lake has a single major tributary flowing from the north, draining Shoshone Lake through the Lewis Channel. At its southern end, the Lewis River flows south to its confluence with the Snake River. Five fish species are currently known to inhabit Lewis Lake: Lake Trout (Salvelinus namaycush), Brown Trout (Salmo trutta), Brook Trout (Salvelinus fontinalis), Utah Chub (Gila atraria), and Redside Shiner (Richardsonius balteatus) (Lewis Lake Historical Record 1977).

Historically, Lewis Lake was fishless due to the impassable Lewis Falls. The lake was first stocked in 1890 by the U.S. Fish Commission to provide a food source for park visitors. Stocking continued until 1941, when 5,890 Lake Trout were introduced. In 1964, Utah Chub were discovered, likely introduced by anglers using live bait, along with Redside Shiner. These species now serve as prey for Lake Trout and Brown Trout. The use of live bait has since been prohibited in Lewis Lake (Lewis Lake Historical Record 1977).

Species of Lewis Lake

Lake Trout

https://www.eekwi.org/animals/fish/lake-trout

Brown Trout

https://www.eekwi.org/animals/fish/brown-trout

Brook Trout

https://www.eekwi.org/animals/fish/brook-trout

Utah Chub

https://fieldguide.mt.gov/speciesDetail.aspx?elcode=AFCJB13020

Methods

A standardized gillnet survey was conducted on Lewis Lake, Yellowstone National Park, from August 26–29, 2019, and August 24–27, 2020, by the National Park Service. Unlike Yellowstone Lake, where annual gillnetting occurs, this type of survey is uncommon on Lewis Lake. Sampling employed two experimental gillnets: one small-mesh gang (0.75–2.0 in mesh) and one large-mesh gang (2.25–3.0 in and 3.5 in mesh), with mesh sizes increasing by 0.25 in across each net (Syslo et al. 2014). Nets were set for a 24-hour soak period.

To account for summer stratification, nets were deployed across three depth strata: at the thermocline (2–10 m), through the thermocline (5–20 m), and below the thermocline (>20 m). Water temperature profiles were recorded to determine stratification timing, which typically occurs in late summer (August).

Biological data collected from each captured fish included total length, weight, sex, maturity stage, and tissue samples.

https://fishionary.fisheries.org/wp-content/uploads/2018/06/gill-net-outline-1024x636.jpg

Sampling Structure

Field sampling took place in 2019 and 2020. Each year four sites were sampled, both years sites 3, 5, and 16 were sampled. In 2019 site 4 was sampled while site 20 was sampled in 2020. The northwestern portion of the lake was not heavily sampled due to being very shallow and covered in underwater dead fall. This is determinant to gillnets.

2019

2020

Combined Years (2019, 2020)

Gillnet Locations

Nets were mapped using latitude and longitude data recorded by the National Park Service.

2019

2020

Combined Years (2019, 2020)

Results

Mean Length of Species in Lewis Lake

Mean total length(mm) was plotted for each species and site with 95% confidence intervals.

2019

2020

Combined Years (2019, 2020)

Fish Catch by Site in Lewis Lake

The total number of each species captured was plotted by site.

2019

2020

Combined Years (2019, 2020)

Catch by Depth Strata

Analysis of catch by depth strata indicates that Brown Trout and Utah Chub occur almost exclusively in nets set at or through the thermocline, whereas Lake Trout are primarily captured in nets set through and below the thermocline.

Catch per unit of effort (C/f)

Catch per unit effort is a metric in fisheries science used to estimate relative abundance and density of a fish population. C/f is calculated by dividing the number of fish caught by the units of effort used to catch them. The National Park Service quantifies a unit of effort by 100m of net per hour. C/f allows us to compare fish abundance over time using standardized assessment netting protocols.

Syslo et al. 2014

Quadrant Assignments

I assigned each site to one of four quadrants within Lewis Lake. This approach allows me to divide the lake into sections, enabling analysis of fish populations in smaller areas and comparison among quadrants to identify potential differences.

Site 4 is located on the border between the SW and SE quadrants. I assigned it to the SW quadrant to maintain sample size consistency across years.

LKT Specific C/f

In order to identify areas with the highest Lake Trout densities, I filtered the data set to include only Lake Trout and applied the same C/f calculations consistent throughout this analysis. 2019 shows wide Lake Trout distribution with hot spots appearing in a majority of nets. 2020 shows fewer hot spots but still a wide distribution. Both years show high densities along the eastern shoreline.

To assess whether non-species specific C/f differed among quadrants, I conducted a Shapiro-Wilk test and a Kruskal-Wallis test. No significant differences were detected in C/f between quadrants.

Shaughnessy, Native Fish Conservation Program, Yellowstone National Park

2019 Lake Trout Specific Analysis

Summary of Tests
Test Statistic p.value
W Shapiro-Wilk 0.782 0.00217
Kruskal-Wallis chi-squared Kruskal-Wallis 5.050 0.16800

2019 Lake Trout Specific Plot

2020 Lake Trout Specific Analysis

Summary of Tests
Test Statistic p.value
W Shapiro-Wilk 0.825 0.00602
Kruskal-Wallis chi-squared Kruskal-Wallis 0.504 0.91800

2020 Lake Trout Specific Plot

All Species C/f

I calculated C/f for all species in Lewis Lake. In 2019 high density clusters appear in the NW and NE quadrants with hot spots throughout the lake, suggesting a wide fish distribution. In 2020 fewer hot spots appear compared to the previous year. The NE quadrant appears to still have a moderate catch.

To assess whether non-species specific C/f differed among quadrants, I conducted a Shapiro-Wilk test and a Kruskal-Wallis test. No significant differences were detected in C/f bewteen quadrants.

2019 All Species Analysis

Summary of Tests (2019)
Test Statistic p.value
W Shapiro-Wilk 0.606 0.00000008694148
Kruskal-Wallis chi-squared Kruskal-Wallis 0.750 0.86127450427952

2019 All Species Plot

2020 All Species Analysis

Summary of Tests (2020)
Test Statistic p.value
W Shapiro-Wilk 0.659 0.000000009681975
Kruskal-Wallis chi-squared Kruskal-Wallis 0.351 0.950191569918547

2020 All Species Plot

Combined Year Comparisons

I mapped 2019 and 2020 together for both Lake Trout specific C/f and All species C/f. Lake Trout appear to be the key driver in congregation areas and appear in high densities along the eastern shore. Other species display a wider distribution across the lake.

Discussion

In 2019, a total of 784 fish were captured, and in 2020, 1,398 fish were captured during gillnet surveys on Lewis Lake. Although Brook Trout are known to occur in the lake, supported by angler-reported sightings in Volunteer Angler Records (VAR), none were captured in these surveys. This absence may be due to their tendency to congregate near tributaries, which were not included among the sampled sites, despite the sampling gear being suitable for their size.

The survey design incorporated three depth strata, allowing for species-specific patterns to emerge. Brown Trout and Utah Chub were typically captured at or through the thermocline, whereas Lake Trout were primarily caught below the thermocline. Utah Chub comprised the majority of individuals captured in both years, with the highest concentrations occurring in the northeast quadrant. This pattern aligns with their spawning behavior and preference for sand or gravel substrates, which dominate that quadrant (Graham 1961).

Lake Trout exhibited the largest mean total length among all species sampled. Utah Chub had the highest catch per unit effort (C/f), while Lake Trout C/f remained moderately consistent across quadrants. Spatial mapping indicated that the eastern shoreline of Lewis Lake had the highest concentration of Lake Trout. This area features a shallow shelf approximately 1m deep extending for about 50m, underlain by rocky cobble substrate. This is ideal spawning habitat for Lake Trout. Beyond this shelf, the lake bottom drops rapidly to depths of roughly 25m. Although Lake Trout typically inhabit deeper waters, they migrate to shallow areas during spawning season, and mapping displayed clusters of Lake Trout along the eastern shore, suggesting individuals are congregating in prime spawning habitat.

Statistical analysis revealed no significant differences in C/f among quadrants for either year, both for Lake Trout specifically and for all species combined. This lack of significance may reflect variability and the relatively small sample size, where sites with higher catch rates could represent random variation rather than true spatial patterns.

Project Extensions

The sampling procedures implemented by the National Park Service provide a strong foundation for future gillnet surveys on Lewis Lake. Expanding these efforts would allow for a larger sample size, enabling a more detailed analysis of species composition and population structure. Future surveys could include additional sampling sites to improve spatial coverage. Notably, the northwest quadrant of the lake was sparsely sampled due to submerged deadfall, which limited gillnet deployment. To address this gap, alternative methods such as rod-and-reel surveys could be employed to gather data from this area and enhance overall understanding of the lake’s fish structure.

Special Thanks

Cody Vender, National Park Service Biologist, Montana State University Fisheries Co-Operative Unit Researcher

Drew MacDonald, National Park Service Biologist, Montana State University Fisheries Co-Operative Unit Researcher

References

McCarrick, D. K., Dillon, J., High, B., & Quist, M. (2022). Spatial and temporal distribution and habitat selection of native Yellowstone Cutthroat Trout and nonnative Utah Chub. U.S. Geological Survey. https://www.usgs.gov/publications/spatial-and-temporal-distribution-and-habitat-selection-native-yellowstone-cutthroat [usgs.gov]

Syslo, J. M., Guy, C. S., Arnold, J. L., Koel, T. M., & Ertel, B. D. (2014). Standard operating procedures for distribution netting in Yellowstone Lake. Retrieved from https://www.researchgate.net/publication/339697733STANDARDOPERATINGPROCEDURESFORDISTRIBUTIONNETTINGINYELLOWSTONE_LAKE [researchgate.net]

Graham, R. J. 1961. Biology of the Utah Chub in Hebgen Lake, Montana. Transactions of the American

Fisheries Society 90:269-276.

Lewis Lake, Historical Record 1977, Yellowstone National Park. Pages 30-32.

https://fishionary.fisheries.org/wp-content/uploads/2018/06/gill-net-outline-1024x636.jpg

https://www.eekwi.org/animals/fish/lake-trout

https://www.eekwi.org/animals/fish/brown-trout

https://www.eekwi.org/animals/fish/brook-trout

https://fieldguide.mt.gov/speciesDetail.aspx?elcode=AFCJB13020