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. 2021 Sep 10;11(9):2661.
doi: 10.3390/ani11092661.

Bobolink (Dolichonyx oryzivorus) Declines Follow Bison (Bison bison) Reintroduction on Private Conservation Grasslands

Affiliations

Bobolink (Dolichonyx oryzivorus) Declines Follow Bison (Bison bison) Reintroduction on Private Conservation Grasslands

Rachel H Kaplan et al. Animals (Basel). .

Abstract

Among the most rapidly declining birds in continental North America, grassland birds evolved with American bison (Bison bison) until bison nearly became extinct due to overhunting. Bison populations have subsequently rebounded due to reintroductions on conservation lands, but the impacts of bison on grassland nesting birds remain largely unknown. We investigated how bison reintroduction, together with other land management and climate factors, affected breeding populations of a grassland bird species of conservation concern, the Bobolink (Dolichonyx oryzivorus). We quantified population changes in Bobolinks over an 18-year period in conservation grasslands where bison were reintroduced, compared with adjacent grasslands grazed by cattle and where hay was harvested after the bird breeding season. Four years after bison reintroduction, the bison population in the study area had doubled, while Bobolink abundance declined 62% and productivity declined 84%. Our findings suggest that bison reintroduction as a conservation strategy may be counterproductive in grassland fragments where overgrazing, trampling, and other negative impacts drive declines in grassland breeding birds. Where bird conservation is an objective, small grassland reserves may therefore be inappropriate sites for bison reintroduction. To maximize conservation benefits to birds, land managers should prioritize protecting grassland birds from disturbance during the bird breeding season.

Keywords: American bison (Bison bison); Bobolink (Dolichonyx oryzivorus); Monitoring Avian Productivity and Survivorship (MAPS); climate change; conservation; domestic cattle (Bos taurus); grasslands; grazing; reintroduction.

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Conflict of interest statement

The authors declare no conflict of interest. The donors who funded this study had no role in the design of the study or in the collection, analyses, or interpretation of data, the writing of the manuscript, or the decision to publish the results.

Figures

Figure 1
Figure 1
Map of the study area showing bird sampling sites in the Platte River Valley, Nebraska, USA. Circles represent ~8 ha sites run 2002–2007; triangles represent ~8 ha sites operated in both 2002–2007 and 2017–2019. Map produced by R.H.K. using ArcGIS software release 10.6, Redlands, CA: Environmental Systems Research Institute.
Figure 2
Figure 2
Boxplot showing Bobolink abundance (unique adult individuals captured/year) before (2002–2007) and after (2017–2019) bison reintroduction (2015) on conservation grasslands in Nebraska, USA. Black lines in boxes represent median values of abundance, while the lower and upper box edges represent the 25th and 75th percentile of the abundance, respectively. Error bars represent the 5th and 95th percentiles of the abundance.
Figure 3
Figure 3
Boxplot showing total Bobolink abundance (unique individuals captured/year) in 2017–2019 on grasslands grazed by bison and cattle compared to grasslands where hay was harvested after the bird breeding season on conservation grasslands in Nebraska, USA. Black lines in each box represent the median value of the abundance, while the lower and upper box edges represent the 25th and 75th percentile of the abundance, respectively. Error bars represent the 5th and 95th percentiles of the abundance.
Figure 4
Figure 4
Bobolink adult abundance in response to time since burning (a), time since grazing (b), January minimum temperature (c) and January precipitation (d) from 2002 to 2019 in Nebraska, USA. Responses to each predictor were estimated using generalized linear mixed models while keeping the value of other predictors constant at their means (0 for standardized variables). The black line represents the mean, while the shaded area corresponds to the 95% confidence interval.
Figure 5
Figure 5
Responses of Bobolink productivity to previous summer temperature (a), January temperature (b), January precipitation (c), months since burning (d) and months since grazing (e) from 2002 to 2019 in Nebraska, USA. Responses to each predictor were estimated using generalized linear mixed models while keeping the value of other predictors constant at their means (0 for standardized variables). The black line represents the mean, while the shaded area corresponds to the 95% confidence interval.

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