Small Grassland Restorations May Not Be Enough to
Restore Local Bird Diversity
Department of Biology, Sacred Heart University, Fairfield, CT
Jonathan Austin & Alexandra Belotti Mentor: J.H. Mattei
Introduction
�
As many as 296 species have been observed at Stratford Point (eBird.org). However, the number of species observed annually has fluctuated over the years 2010-2021, ranging from as low as 132 species in 2014 to as many as 214 species in 2015 (Fig. 3). In fact, this was the most drastic 1-year change with a 62% increase in species. In contrast, there was a 32% decrease from 2018-2019 (Fig. 3). Similar fluctuations can be observed for Bobolinks (D. oryzivorus) and Savannah Sparrows (P. sandwichensis) (Figs. 5 & 6). Spring and fall migrations change as well (Fig. 4). There is a large spring migration in 2015, but this migration is missing in 2010 and 2021. Fall migration occurred in all years reported on Fig. 4, with slight timing variations. For instance, fall migration peaked in Aug. of 2010, Oct. of 2015, and Sept. of 2021. Lastly, the number of the observations submitted on eBird has dramatically decreased (Fig. 2). In 2015, 409 observations were submitted to eBird pertaining to important grassland species including the Bobolink (D. oryzivorus), Eastern Meadowlark (S. magna), Savannah Sparrow (P. sandwichensis), Grasshopper Sparrow (A. savannarum) and more (Fig. 2). 2021 had 104 observations, only a quarter of the observations in 2015. Overall, the data showed 2015 was the most diverse year, and July through Oct. is the busiest and most diverse time of year.
Figure 8. Mugwort at Stratford Point (Artemisia vulgaris)
Methods
Grassland Restoration
Bird Data Collection
Bird diversity was evaluated using observations obtained from eBird (ebird.org) from 2010 through 2021 to determine trends in the number of species and species abundance in response to remediation of the site We also examined 2 specific species that are known to inhabit grasslands in Connecticut (Figures 6 and 7).
�
Results
References
Dauber, J., Hirsch, M., Simmering, D., Waldhardt, R., Otte, A., and Wolters, V. (2003). Landscape structure as an indicator of biodiversity: matrix effects on species richness. Agric. Ecosyst. Environ. 98, 321–329.
Folsom-O’Keefe C., Mattei J., Leenders T., Hauser C. 2021. Stratford Point Coastal Habitat Management Plan.
Haddad, N. M., Brudvig, L. A., Clobert, J., Davies, K. F., Gonzalez, A., Holt, R. D., et al. (2015). Appliedecology: habitat fragmentation and its lasting impact on Earth’s ecosystems. Sci. Adv
Kroll, A. J., Ren, Y., Jones, J. E., Giovanini, J., Perry, R. W., Thill, R. E., et al. (2014). Avian community composition associated with interactions between local and landscape habitat attributes. For. Ecol. Manage. 326, 46–57.
Silva TW, Fontana CS. 2021. Remnants of Native Vegetation Surrounding Do Not Affect the Diversity and Density of Birds in Brazilian Grassland-Restoration Sites. Fron. Ecol. and Evol. 8: 1-7.
Forest Service, Pacific Northwest Region. 1996. Triclopyr: Herbicide Information Profile. United States Department of Agriculture.
�
Figure 4. Bird species counts by month in 2010, 2015, and 2021..
Figure 2. Number of eBird observations in 2015 and 2021
Figure 6. Savannah Sparrow (Passerculus sancwichensis) counts by year
Figure 7. Bobolink (Dolichonyx oryzivorus) counts by year
Click to add te
Discussion
Photo Credit: Bryan Calk. 6 Jan 2019, Macaulay Library, eBIrd.org
Photo Credit: Ryan Sanderson. 3 July 2020, Macaulay Library, eBird.org
Figure 3. Bird species counts by year
Figure 5. Coastal grasslands populated with Switchgrass (Panicum virgatum) and Indiangrass (Sorghastrum nutans)
Figure 1. Location of Stratford Point Grassland Site