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Original Articles

Using standardized fishery data to inform rehabilitation efforts

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Figures & data

Figure 1 Location of Smith Lake, Two Rivers Lake #1, and Yankee Hill in Nebraska. The star size reflects the relative size of the lakes to one another.
Figure 1 Location of Smith Lake, Two Rivers Lake #1, and Yankee Hill in Nebraska. The star size reflects the relative size of the lakes to one another.

Table 1 Comparison of catch per unit effort in 3 Nebraska waterbodies pre- and post- rehabilitation for largemouth bass (fish/h electrofishing) and bluegill (fish/net-night). Comparisons were made within size groups derived from Gabelhouse (Citation1984). The length groups assessed were stock-length (S) fish, stock- to quality-length (S-Q) fish, quality- to preferred-length (Q-P) fish, preferred- to memorable-length (P-M) fish, and memorable- to trophy-length (M-T) fish. Welch's one-tailed t-tests were used in all comparisons. ND denotes inadequate data to carry out the test and * denotes significant result.

Table 2 Statistical results of comparison (Kolmogorov–Smirnov test) of length distributions in three Nebraska waterbodies pre- and post-rehabilitation. Length distribution data were grouped across years for each period (i.e., pre- and post- rehabilitation). The alternative hypothesis for each test was that the pre-rehabilitation length distribution was less than the post-rehabilitation length data. ND denotes inadequate data to carry out the test.

Figure 2 Largemouth bass and bluegill size structure pre- (top) and post-rehabilitation (bottom) in Two Rivers Lake #1, Nebraska. Nighttime electrofishing occurred 1997–2001, 2003, 2007, and 2009 (largemouth bass data), and frame netting occurred 1997–2001 and 2003 (bluegill data).
Figure 2 Largemouth bass and bluegill size structure pre- (top) and post-rehabilitation (bottom) in Two Rivers Lake #1, Nebraska. Nighttime electrofishing occurred 1997–2001, 2003, 2007, and 2009 (largemouth bass data), and frame netting occurred 1997–2001 and 2003 (bluegill data).

Table 3 Comparison of pre- and post-rehabilitation catch per unit effort (CPUE ± 95% CI) and the CPUE estimates for lakes and reservoirs of similar type across Nebraska (ecosystem CPUE ± 95% CI). A single ecosystem CPUE value (i.e., control) was used that incorporated the long-term variability in each ecosystem type including sandpit or dugout lakes, Sandhill ecoregion lakes, and flood control reservoirs. The t-value is calculated by comparing 2 means with degrees of freedom (df) and the P-value associated with each test. A t-value greater than the critical t-value of 1.96 indicates a statistically significant difference between the means. * indicates a change in CPUE occurred between pre- and post-rehabilitation compared to the long-term ecosystem average; ND denotes inadequate data to carry out the test.

Figure 3 Largemouth bass and bluegill size structure during pre- (top) and post-rehabilitation (bottom) in Smith Lake, Nebraska. Nighttime electrofishing occurred 1994–1997, 2000, 2002, 2003, 2005, 2007, and 2011 (largemouth bass data), and frame netting occurred 1994, 1996–2008, 2010, and 2011 (bluegill data).
Figure 3 Largemouth bass and bluegill size structure during pre- (top) and post-rehabilitation (bottom) in Smith Lake, Nebraska. Nighttime electrofishing occurred 1994–1997, 2000, 2002, 2003, 2005, 2007, and 2011 (largemouth bass data), and frame netting occurred 1994, 1996–2008, 2010, and 2011 (bluegill data).
Figure 4 Largemouth bass and bluegill bass size structure during pre- (top) and post-rehabilitation (bottom) in Yankee Hill Reservoir, Nebraska. Note different scales on figure axes. Nighttime electrofishing occurred 1998–2000, 2008, 2009, and 2010 (largemouth bass data), and frame netting occurred 1998–2010 (bluegill data).
Figure 4 Largemouth bass and bluegill bass size structure during pre- (top) and post-rehabilitation (bottom) in Yankee Hill Reservoir, Nebraska. Note different scales on figure axes. Nighttime electrofishing occurred 1998–2000, 2008, 2009, and 2010 (largemouth bass data), and frame netting occurred 1998–2010 (bluegill data).

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