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Evaluating At-Risk Black Ash Wetlands as Biodiversity Hotspots in Northern Forests

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Abstract

Black ash (Fraxinus nigra) forests, which cover over 1.2 million hectares in the Great Lakes Region, are threatened by emerald ash borer (EAB; Agrilus planipennis), which is eliminating native populations of ash throughout the region. Understanding the contribution of black ash wetlands to local and regional species richness is critical in forming effective conservation policies and informing management plans for these imperiled habitats. We measured breeding bird and anuran communities in black ash wetlands and compared them to nearby non-black ash habitats for each taxa: aspen-dominated upland forest for birds and emergent wetlands for anurans. Our results showed black ash wetlands support unique communities of birds but not of anurans. For birds, black ash wetlands had higher species richness and a greater number of birds that were indicator species compared to upland forests; this is likely due the presence of a water component and more structural diversity in black ash wetlands compared to aspen-dominated aspen forests. In contrast, emergent wetlands had higher richness of breeding anurans and greater number indicator species than black ash wetlands; this reflects a general preference by North American anurans to breed in more open canopy habitats. If EAB invades these systems, expected increases in ponding and canopy openness may be beneficial for some anuran species during the breeding season, but loss of the forest canopy could result in significant changes in bird community composition. Our results indicate that implementing management strategies that focus on emulating structural complexity of black ash wetlands will be beneficial for conserving wildlife diversity.

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Data Availability

A long-term data sharing and preservation plan will be used to store and make publicly accessible the data beyond the life of the project. The data will be deposited into the Data Repository for the University of Minnesota (DRUM). A persistent link will be added to the manuscript if accepted into the journal.

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Acknowledgements

Special thanks to Katy Johnson, Josh Bednar, and Steve Kolbe for wildlife data collection. Thanks to Michael Joyce for assistance developing lidar variables. We also thank the USDA Forest Service Chippewa National Forest, county land managers, and Minnesota Department of Natural Resources for providing the sites used in this research. This publication is Natural Resources Research Institute contribution number ###.

Funding

Funding for the implementation of the study design and wildlife surveys was provided by the Minnesota Environment and Natural Resources Trust Fund as recommended by the Legislative-Citizen Commission on Minnesota Resources (LCCMR). Additional support for this work came from the Upper Midwest and Great Lakes Landscape Conservation Cooperative, Department of Interior Northeast Climate Adaptation Science Center, and USDA Forest Service Northern Research Station.

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Contributions

All authors contributed to the study conception and design. ARG and MBY designed the wildlife survey methods, conducted the investigation, and analyzed the data. ARG, MBY, RAS, wrote the manuscript, and AWD and BPP provided editorial advice and valuable insight. ARG, RAS, AWD, and BPP were involved with funding acquisition.

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Correspondence to Alexis R. Grinde.

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Appendices

Appendix 1

Table 3

Table 3 List of bird species detected within 100 m radius during point counts. Common name, scientific name, nest location, primary diet, and primary breeding habitat along with observed abundance in black ash wetlands and upland forests are provided. Nest, diet, and habitat assignments were sourced from Niemi et al. (2016) and Billerman et al. (2020)

Appendix 2

Table 4

Table 4 List of anuran species detected during surveys. Common name, scientific name, timing of breeding, breeding wetland status, and percent of sites each species was detected in black ash wetlands and emergent wetlands are provided. Breeding ecology classifications were sourced from Lannoo 2005

Appendix 3

Figure 3

Fig. 3
figure 3

Species correlation matrices for anuran (A.) and bird (B.) JSDM latent variable models. A.) Anuran species correlations for presence/absence. B.) Breeding bird species correlations; see Appendix 1 Table 3 for bird species abbreviation codes. Red indicates a positive correlation

Appendix 4

Table 5

Table 5 Mean canopy height coefficient estimates and 95% confidence interval from multivariate community analyses. Bolded species have coefficients different from zero

Appendix 5

Table 6

Table 6 Results of generalized linear models used to assess relationship between bird species richness and total abundance and anuran species richness and environmental variables. Models that were significantly different from null models are bolded

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Grinde, A.R., Youngquist, M.B., Slesak, R.A. et al. Evaluating At-Risk Black Ash Wetlands as Biodiversity Hotspots in Northern Forests. Wetlands 42, 122 (2022). https://doi.org/10.1007/s13157-022-01632-9

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