Ecology and Vulnerability
Blanding's Turtle
Photo credit: Bill Byrne, MassWildlife
Profile: Blanding's Turtle ▾▸
Background
The Blanding’s turtle's range is centered in the Great Lakes region and west to Nebraska, but there are also three disjunct populations in New York, eastern Massachusetts into southern...
Background
The Blanding’s turtle's range is centered in the Great Lakes region and west to Nebraska, but there are also three disjunct populations in New York, eastern Massachusetts into southern Maine, and southern Nova Scotia1,2. Habitat fragmentation and road kill mortality2,3 appear to be causing a decline in populations. Such mortality can significantly impact populations because the species is very long-lived (70+ years), has delayed sexual maturity, and low fecundity or fertility1,4. As a result, the species is listed as "at risk" in 17 of 18 states or provinces across its range3. In Massachusetts, it is currently listed as "threatened"2.
The Blanding’s turtle is generally considered a northern species that inhabits productive wetlands including ponds, creeks, and marshes5,6. Compared to more southern turtle species, it tolerates lower maximum temperatures and seeks out microhabitats that result in lower body temperatures5. Though largely aquatic, it can make long overland movements for nesting7. The species has a relatively large home size and will travel extensively between wetlands2,6. Females nest in upland locations with nesting peaking in June4,8. Turtles move to overwinter locations in September and October and remain moderately active until ice formation6. They emerge from hibernation under the ice between March and April9.
Climate Impacts
Blanding’s turtles inhabit a fairly narrow latitudinal range10. They are restricted by temperatures at the northern and southern boundaries1,3, and have a relatively low tolerance for high temperatures5,7. This suggests that their optimal climatic range will likely shift north as climate changes. However, the ability of Blanding’s turtles to move north with such changes may be hampered by habitat fragmentation, as road crossings are hazardous and vehicles cause significant mortality3,4. Habitat suitability for Blanding’s turtles decreases rapidly as road density increases3.
Temperature can also impact male to female ratios, as some turtles, including Blanding’s turtle, exhibit temperature-dependent sex determination10. In such turtles, temperature changes during incubation of eggs can alter sex ratios. However, to date, studies have failed to find any connection between changing climate and sex ratios in populations that are known to have experienced warming temperatures10.
Additionally, climate change is projected to increase the frequency of short-term summer drought conditions in the Northeast11. This has the potential to impact turtles through reduction of suitable habitat. In some populations, Blanding’s turtles have been observed to reduce activity during drought conditions, and to prepare for hibernation earlier in the season7.
1. Spooner, I., S. Stolze, B. Martin, A. Robichaud, T. Herman, S. Mockford, B. Caverhill, D. Mazzucchi, and H. White. 2014. A 10,000-year record of environmental change from Blanding’s turtle (Emydoidea blandingii) habitat at Pleasant River fen, Nova Scotia, Canada. Wetlands 34:1145-1158.
3. Millar, C.S., and G. Blouin-Demers. 2012. Habitat suitability modelling for species at risk is sensitive to algorithm and scale: a case study of Blanding’s turtle, Emydoidea blandingii, in Ontario, Canada. Journal for Nature Conservation 20:18-29.
4. Markle, C.E., and P. Chow-Fraser. 2014. Habitat selection by the Blanding’s turtle (Emydoidea blandingii) on a protected island in Georgian Bay, Lake Huron. Chelonian Conservation and Biology 13:216-226.
5. Sajwaj, T.D., and J.W. Lang. 2000. Thermal ecology of Blanding’s turtle in central Minnesota. Chelonian Conservation and Biology 3:626-636.
6. Edge, C.B., B.D. Steinberg, R.J. Brooks, and J.D. Litzgus. 2009. Temperature and site selection by Blanding’s Turtles (Emydoidea blandingii) during hibernation near the species’ northern range limit. Canadian Journal of Zoology 87:825-834.
7. Anthonysamy, W.J.B., M.J. Dreslik, and C.A. Phillips. 2013. Disruptive influences of drought on the activity of a freshwater turtle. The American Midland Naturalist 169:322-335.
8. Innes, R.J., K.J. Babbitt, and J.J. Kanter. 2008. Home range and movement of Blanding's turtles (Emydoidea blandingii) in New Hampshire. Northeastern Naturalist 15:431-444.
9. Thiel, R.P., and T.T. Wilder. 2010. Over-wintering characteristics of west-central Wisconsin Blanding’s turtles, Emydoidea blandingii. Canadian Field-Naturalist 124:134-138.
10. Reid, B.N., and M.Z. Peery. 2014. Land use patterns skew sex ratios, decrease genetic diversity and trump the effects of recent climate change in an endangered turtle. Diversity and Distributions 20:1425-1437.
11. Huntington, T.G., A.D. Richardson, K.J. McGuire, and K. Hayhoe. 2009. Potential impacts of global climate change on the hydrology and ecology of ephemeral freshwater systems of the forests of the northeastern United States. Canadian Journal of Forest Research 39:199-212.