Ecology and Vulnerability
Northern Long-eared Bat

Image
Northern Long-eared Bat (Myotis septentrionalis)

Photo credit: U.S. Fish and Wildlife Service

Scientific name
Myotis septentrionalis

Profile: Northern Long-Eared Bat

Background
The northern long-eared bat, also commonly called the northern myotis, is found in Canada (from British Columbia to southern Quebec and Newfoundland) and the US (its range extends south to...

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Background
The northern long-eared bat, also commonly called the northern myotis, is found in Canada (from British Columbia to southern Quebec and Newfoundland) and the US (its range extends south to Oklahoma and east to South Carolina)1,2.  Northern long-eared bats eat insects in the forest interior3,4.  Bats begin to emerge from hibernation in April and Mayin northern areas and as early as March in southern areas1.  During summer, northern long-eared bats can be found in trees during the day. They leave their resting trees to feed immediately after sunset and return to rest again immediately before sunrise4,6.

Previously, this species was frequently seen in the northeastern US.  More recently, however, many bats have died as a result of a fungus that causes white nose disease7.  This disease is currently the greatest cause of death in wintering northern long-eared bats5.  In 2013 and 2014, surveys of known hibernation sites in Massachusetts found zero or one northern long-eared bat per site, much lower than is considered normal7.  In 2015, the US Fish and Wildlife Service labeled the northern long-eared bat “threatened” under the Endangered Species Act7.

Climate Impacts
Bats must store enough energy reserves over the summer to enable them to survive winter hibernation8.  Changes in precipitation and temperature are likely to have effects on the availability of the insects they eat and thus on their stored energy reserves9.  Additionally, it is possible that warmer temperatures could cause bats to wake up from hibernation more often, which takes more energy9.  Moreover, stored energy reserves are depleted at a rate that is dependent on the temperature of the hibernaculum (shelter where they hibernate), with temperatures above or below 2°C/36°F increasing the rate of depletion8.  On the other hand, a longer growing season is likely to reduce the length of time that they hibernate. 

It is unclear how these climate change effects will interact to influence bats.  However, models based on energy needs related to hibernation conditions correctly predicted the distribution of the little brown bat in Canada (a northward range shift over the next century)8.  Based on these models, similar range shifts are anticipated for other bat species, including the northern long-eared bat.

References

1. Thompson, F.R. 2006. Conservation assessments for five forest bat species in the Eastern United States. General Technical Report NC-260. U.S. Department of Agriculture, Forest Service, North Central Research Station. St. Paul, MN. 82 p.

2. Burns, L.E., J.L. Segers, and H.G. Broders. 2015. Bat activity and community composition in the northern boreal forest of south-central Labrador, Canada. Northeastern Naturalist 22:32-40.

3. Broders, H.G., L.J. Farrow, R.N. Hearn, L.M. Lawrence, and G.J. Forbes. 2014. Stable isotopes reveal that little brown bats have a broader dietary niche than northern long-eared bats. Acta Chiropterologica 16:315-325.

4. Johnson, J.B., J.W. Edwards, and W.M. Ford. 2011. Nocturnal activity patterns of northern myotis (Myotis septentrionalis) during the maternity season in West Virginia (USA). Acta Chiropterologica 13:391-397.

5. Frank, C.L., A. Michalski, A.A. McDonough, M. Rahimian, R.J. Rudd, and C. Herzog. 2014. The resistance of a North American bat species (Eptesicus fuscus) to white-nose syndrome (WNS). PloS ONE 9(12):e113958.

6. Johnson, J.B., W.M. Ford, and J.W. Edwards. 2012. Roost networks of northern myotis (Myotis septentrionalis) in a managed landscape. Forest Ecology and Management 266:223-231.

7. DOI. 2015. Endangered and Threatened Wildlife and Plants; Threatened Species Status for the Northern Long-Eared Bat With 4(d) Rule. Federal Register 80 (2 April 2015), pp. 17974-18033.

8. Humphries, M.M., D.W. Thomas, and J.R. Speakman. 2002. Climate-mediated energetic constraints on the distribution of hibernating mammals. Nature 418:313-316.

9. Rodenhouse, N.L., L.M. Christenson, D. Parry, and L.E. Green. 2009. Climate change effects on native fauna of northeastern forests. Canadian Journal of Forest Research 39:249-263.

Climate Change Vulnerability Assessment: Northern Long-eared Bat (Maryland)

Ranking
Vulnerable
Confidence
Not Specified
Climate scenario
Not Specified
Location
Maryland
Time period
Not Specified

Climate Change Vulnerability Assessment: Northern Long-eared Bat (Fort Drum, NY)

Ranking
Vulnerable
Confidence
Not Specified
Climate scenario
Changes in temperature and moisture, sea level rise
Location
Fort Drum, NY
Time period
2050

Climate Change Vulnerability Assessment: Northern Long-eared Bat (Tennessee)

Ranking
Presumed Stable
Confidence
Incorporated into the CCVI method
Climate scenario
"Climate Wizard projections for 2050; IPCC Fourth Assessment Report (IPCC 2007) for a 16-model Ensemble Average "
Location
Tennessee
Time period
2050

Climate Change Vulnerability Assessment: Northern Long-eared Bat (Massachusetts)

Ranking
Vulnerable
Confidence
The experts assessing traits also scored their level of uncertainty
Climate scenario
"The study used climate data from two models: the Community Earth System Model (CESM) and the Model for Interdisciplinary Research on Climate (MIROC5). "
Location
Massachusetts
Time period
2070

Climate Change Vulnerability Assessment: Northern Long-eared Bat (Ontario, Canada)

Ranking
Vulnerable
Confidence
The study quantified uncertainty by conducting sensitivity analyses. Uncertainty in available data and/or limits to current knowledge about biological traits is factored in by scoring multiple categories for a single sensitivity factor.
Climate scenario
"The study used three General Circulation Models (GCMs) - CanESM2, HadGEM2-ES, and MIROC5."
Location
Ontario, Canada
Time period
2041–2071

Climate Change Vulnerability Assessment: Northern Long-eared Bat (Entire Range of sp.)

Ranking
Vulnerable
Confidence
Not Specified
Climate scenario
Not Specified
Location
Entire Range of Species
Time period
Not Specified

Climate Change Vulnerability Assessment: Northern Long-eared Bat (Michigan)

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