Ecology and Vulnerability
Wood Turtle

Image
Wood Turtle (Glyptemys insculpta)

Photo credit: Bill Byrne, MassWildlife

Scientific name
Glyptemys insculpta

Profile: Wood Turtle

Background
The wood turtle is closely associated with rivers and streams, spending the majority of its time in the water1.  However, during the active period of summer, it may spend considerable time...

Read More

Background
The wood turtle is closely associated with rivers and streams, spending the majority of its time in the water1.  However, during the active period of summer, it may spend considerable time away from water foraging for food, even becoming mostly terrestrial for periods of time2,3.  These forays into the landscape can make it vulnerable to mortality from road crossings, agricultural machinery, and mammal attacks4.  In addition, wood turtles are highly sought by collectors3.  Because the species is long lived (up to 58 years) and has low reproductive rates, loss of individuals can greatly impact populations1,3.  Increased fragmentation of habitat and human disturbance has led to declines throughout the range and the species is currently listed as endangered on the IUCN Red List5.  

Climate Impacts
As with other reptiles, wood turtles have limited physiological control over body temperature and must regulate their temperature through habitat selection and behavior6.  Wood turtles will bask in the sun to raise their body temperature and the amount of time spent basking appears to decrease during the warmer months (July and August)6,7. When turtles start basking in the spring is related to air temperature and will begin when a certain temperature threshold is reached.  Air temperature thus directly controls the length and intensity of the active period for wood turtles.  Ambient temperature also appears to play a role in terrestrial activity.  More time spent basking decreases the amount of time spent foraging in the landscape6, but turtles also will retreat to a stream when air temperatures are cool, using the water as a thermal (temperature) refuge 6,8

In northern populations, these requirements for thermoregulation (maintaining body temperature) limit the spatial distribution of turtles so that terrestrial activity is decreased6.  In these populations, turtles will remain closer to streams, using water as a thermal refuge as nighttime temperatures fall6,9,10.  Additionally, length of winter hibernation is related to climate3.  Because behavior is so closely tied to temperature in this species, it seems likely that climate change could directly affect behavior, though population responses are unknown.  However, one study found that clutch frequency (rate that batches of eggs are laid) increased with increasing autumn temperatures in a northern population of painted turtles, suggesting potential effects on reproductive output11.  It is possible that increased terrestrial activity associated with higher temperatures could also increase harmful interactions with humans.

Additionally, wood turtles may be displaced up to several kilometers downstream during flood events4,12.  Increases in precipitation, especially rain, during winter are projected for the Northeast, potentially resulting in increased frequency and severity of high flow flood events during this period13,14,15.  A study of wood turtles in Massachusetts showed that floods displaced nearly half of the subpopulation annually, resulting in elevated mortality rates and decreased breeding success12.

References

1. Hunter, M.L, A.J.K. Calhoun, and M. McCollough. 1999. Wood Turtle Clemmys insculpta. Pages 138-143 in Maine Amphibians and Reptiles. The University of Maine Press, Orono, ME.

2. Ernst, C.H. 1986. Environmental temperatures and activities in the wood turtle, Clemmys inscuplta. Journal of Herpetology 20:222-229.

3. Harding, J.H., and T.J. Bloomer. 1979. The Wood Turtle, Clemmys insculpta—a natural history. Bulletin of New York Herpetological Society 15:9-26.

4. Parren, S.G. 2013. A twenty-five year study of the wood turtle (Glyptemys inscuplta) in Vermont: movements, behavior, injuries, and death. Herpetological Conservation and Biology 8:176-190.

5. van Dijk, P.P., and J. Harding. 2013. Glyptemys insculpta. The IUCN Red List of Threatened Species. Version 2014.3. <http://www.iucnredlist.org/details/4965/0>. (Accessed on 15 May 2015).

6. Dubois, Y., G. Blouin-Demers, B. Shipley, and D. Thomas. 2009. Thermoregulation and habitat selection in wood turtles Glyptemys insculpta: chasing the sun slowly. Journal of Animal Ecology 78:1023-1032.

7. Compton, B.W., J.M. Rhymer, and M. McCollough. 2002. Habitat selection by wood turtles (Clemmys insculpta): an application of paired logistic regression. Ecology 83:833-843.

8. Kaufmann, J.H. 1992. Habitat use by wood turtles in central Pennsylvania. Journal of Herpetology 26:315-321.

9. Arvisais, M., E. Lévesque, J.C. Bourgeois, C. Daigle, D. Masse, and J. Jutras. 2004. Habitat selection by the wood turtle (Clemmys insculpta) at the northern limit of its range. Canadian Journal of Zoology 82:391-398.

10. Remsberg, A.J., T.L. Lewis, P.H. Huber, and K.A. Asmus. 2006. Home ranges of wood turtles (Glyptemys insculpta) in northern Michigan. Chelonian Conservation and Biology 5:42-47.

11. Rollinson, N., and R.J. Brooks. 2007. Proximate constraints on reproductive output in a northern population of painted turtles: an empirical test of the bet-hedging paradigm. Canadian Journal of Zoology 85:177-184.

12. Jones, M.T., and P.R. Sievert. 2009. Effects of stochastic flood disturbance on adult wood turtles, Glyptemys insculpta, in Massachusetts. Canadian Field-Naturalist 123:313-322.

13. Huntington, T.G., A.D. Richardson, K.J. McGuire, and K. Hayhoe. 2009. Climate and hydrological changes in the northeastern United States: recent trends and implications for forested and aquatic ecosystems. Canadian Journal of Forest Research 39:199-212.

14. Meehl, G.A., J.M. Arblaster, and C. Tebaldi. 2005. Understanding future patterns of increased precipitation intensity in climate model simulations. Geophysical Research Letters 32: doi:10.1029/2005GL023680.

15. Hayhoe, K., C. Wake, B. Anderson, X.Z. Liang, E. Maurer, J. Zhu, J. Bradbury, A. DeGaetano, A.M. Stoner, and D. Wuebbles. 2008. Regional climate change projections for the Northeast USA. Mitigation and Adaptation Strategies for Global Change 13:425-436.

Climate Change Vulnerability Assessment: Wood Turtle (Maine)

Ranking
Presumed Stable
Confidence
Moderate
Climate scenario
Not specified
Location
Maine
Time period
Not specified

Climate Change Vulnerability Assessment: Wood Turtle (Vermont)

Ranking
Vulnerable
Confidence
High
Climate scenario
Not specified
Location
Vermont
Time period
2050-2100

Climate Change Vulnerability Assessment: Wood Turtle (New York)

Ranking
Presumed stable
Confidence
High
Climate scenario
SRES A1B (Mid-range emissions scenario)
Location
New York
Time period
2050

Climate Change Vulnerability Assessment: Wood Turtle (Northern Appalacians & Maritime Canada)

Ranking
Presumed Stable
Confidence
High
Climate scenario
SRES A1B (Mid-range emissions scenario)
Location
Northern Appalacians & Maritime Canada
Time period
2050

Climate Change Vulnerability Assessment: Wood Turtle (North Atlantic Coast)

Ranking
Presumed Stable
Confidence
Very High
Climate scenario
SRES A1B (Mid-range emissions scenario)
Location
North Atlantic Coast
Time period
2050

Climate Change Vulnerability Assessment: Wood Turtle (Mid-Atlantic Coast)

Ranking
Presumed Stable
Confidence
Very High
Climate scenario
SRES A1B (Mid-range emissions scenario)
Location
Mid-Atlantic Coast
Time period
2050

Climate Change Vulnerability Assessment: Wood Turtle (Michigan)

Ranking
Moderately Vulnerable
Confidence
Moderate
Climate scenario
SRES A1B (Mid-range emissions scenario)
Location
Michigan
Time period
2050

Climate Change Vulnerability Assessment: Wood Turtle (Pennsylvania)

Ranking
Presumed stable
Confidence
Moderate
Climate scenario
SRES A1B (Mid-range emissions scenario)
Location
Pennsylvania
Time period
2050