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Open-File Report 2010–1020

In cooperation with the U. S. Army Corp of Engineers

The Power to Detect Trends in Missouri River Fish Populations within the Pallid Sturgeon Population Assessment Program

By Janice L. Bryan, Mark L. Wildhaber, Dan Gladish, Scott Holan, and Mark Ellerseick

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Executive Summary

As with all large rivers in the United States, the Missouri River has been altered, with approximately 32.5 percent of the main stem length impounded and 32.5 percent channelized. These physical alterations to the environment have had effects on the fisheries, but studies examining the effects of alterations have been localized and for short periods of time. In response to the U.S. Fish and Wildlife Service biological opinion, the U.S. Army Corps of Engineers initiated monitoring of the fish community of the Missouri River in 2003. The goal of the Pallid Sturgeon Population Assessment Program is to provide information to detect changes in populations and habitat preferences with time for pallid sturgeon (Scaphirhynchus albus) and native target species in the Missouri River Basin. To determine statistical power of the Pallid Sturgeon Population Assessment Program, a power analysis was conducted using a normal linear mixed model with variance component estimates based on the first 3 years of data (2003 to 2005). In cases where 3 years of data were unavailable, estimates were obtained using those data. It was determined that at least 20 years of data, sampling 12 bends with 8 subsamples per bend, would be required to detect a 5 percent annual decline in most of the target fish populations. Power varied between Zones. Zone 1 (upstream from Lake Sakakawea) did not have any species/gear type combinations with adequate power, whereas Zone 3 (downstream from Gavins Point Dam) had 19 species/gear type combinations with adequate power. With a slight increase in the sampling effort to 12 subsamples per bend, the Pallid Sturgeon Population Assessment Program has adequate power to detect declines in shovelnose sturgeon (S. platorynchus) throughout the entire Missouri River because of large catch rates. The lowest level of non-occurrence (in other words, zero catches) at the bend level for pallid sturgeon was 0.58 using otter trawls in Zone 1. Consequently, the power of the pallid sturgeon models was not as high as other species at the current level of sampling, but an increase in the sampling effort to 16 subsamples for each of 24 bends for 20 years would generate adequate power for the pallid sturgeon in all Zones. Since gear types are selective in their species efficiency, the strength of the Pallid Sturgeon Population Assessment Program approach is using multiple gears that have statistical power to detect population trends at the same time in different fish species within the Missouri River. As often is the case with monitoring studies involving endangered species, the data used to conduct the analyses exhibit some departures from the parametric model assumptions; however, preliminary simulations indicate that the results of this study are appropriate.

First posted June 14, 2010

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Suggested citation:

Bryan, J. L., M. L. Wildhaber, D. Gladish, S. Holan, M. Ellerseick, 2010, The power to detect trends in Missouri River fish populations within the Pallid Sturgeon Population Assessment Program: U.S. Geological Survey Open-File Report 2010–1020, 414 p.



Contents


Executive summary

Introduction

Methods

Results

Conclusions

Acknowledgments

References

Appendix A. Comparisons of data versions with QA/QC progression

Appendix B. Groups of data that were removed due to the criteria defined in the methods

Appendix C. Results of the power analysis at different annual population decreases for a sampling level of 12 bends and 8 subsamples for 5 years

Appendix D. Results of the power analysis at different annual population decreases for a sampling level of 12 bends and 8 subsamples for 10 years

Appendix E. Results of the power analysis at different annual population decreases for a sampling level of 12 bends and 8 subsamples for 20 years

Appendix F. Illustrated results of the power analysis at different annual population decreases for multiple subsample and bend levels, summarized by zone, season, segment, and gear type

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