Eastern Red Bat (Lasiurus borealis) Chris Harshaw

Eastern Red Bat (Lasiurus borealis)
Chris Harshaw

Mammalia (Mammals)
Vespertilionidae (Evening Bats and Vesper Bats)
State Protection
Not Listed
Not listed or protected by New York State.
Federal Protection
Not Listed
State Conservation Status Rank
Vulnerable in New York, or Apparently Secure – Vulnerable to disappearing from New York (but not currently imperiled), with relatively few populations or locations, few individuals, and/or restricted range; or uncommon but not rare in New York; may be rare in some parts of the state; possibly some cause for long-term concern due to declines or other factors. More information is needed to assign either S3 or S4. (A migratory animal which occurs in New York only during the breeding season.)
Global Conservation Status Rank
Vulnerable globally, or Apparently Secure - At moderate risk of extinction, with relatively few populations or locations in the world, few individuals, and/or restricted range; or uncommon but not rare globally; may be rare in some parts of its range; possibly some cause for long-term concern due to declines or other factors. More information is needed to assign either G3 or G4.


Did you know?

Eastern red bats may live close to moderately populated areas and are known to forage for insects around street lights.

State Ranking Justification

Eastern red bats are not rare in the state and so are not tracked by The New York Natural Heritage Program. They occur in the state in the summer, migrate out of the state in the winter, and travel through during migration. They are regularly encountered statewide during acoustic surveys conducted by NYSDEC and this monitoring documented stability in their distribution over the short-term.  Population trends of eastern red bats in New York are unknown and this information is needed to accurately assess threats to the species in the state. They are not as common in New York as in states farther south, and in some parts of their range such as in Michigan (Winhold et al. 2008), there is evidence that they could be declining.

Short-term Trends

The short-term trends in New York distribution appear to be stable from 2009-2013 (NYSDEC unpub. data) and the populations trends are unknown.

Long-term Trends

The long-term trends are not known for New York. There is evidence that this species could be declining in at least parts of its range (Winhold et al. 2008).

Conservation and Management

Conservation Overview

Eastern red bats are regularly encountered in New York and may occur in a variety of habitats and sometimes in proximity to moderate human densities. They are killed during collisions with wind turbines during the late-summer/early-fall migration period and it is not yet known whether this is a threat to the persistence of healthy populations in New York.


Red bats are migratory tree bats that migrate rather than congregate in caves over the winter, and are not known to be affected by white-nose syndrome which has devastated cave bat populations in eastern North America. The incidence of rabies in eastern red bats is moderate to high and may be of concern in some regions. Studies report the incidence of rabies among submitted carcasses as 11% in Indiana (Whitaker and Douglas 2006) and 5% in New York (Childs et al. 1994).
Red bats are killed when they collide with wind turbines in New York, particularly during fall migration. It is unknown whether the numbers of bats killed at turbines during migration is high enough to impact population numbers in the state. One study reported that red bats made up to 61% of bat carcasses found at wind facilities in the eastern U.S (Arnett et al. 2008).
Bats may be particularly sensitive to environmental toxins including those found in herbicides and pesticides. They are highly susceptible to DDT residue and this chemical was widely used as a pesticide to control bat infestations in houses in the 1940s (U.S. Geological Survey 2013). It was also widely used (including aerial application) to control mosquitoes and agricultural pests in the 1940s and 50s. It was banned with few exceptions in 1972. Since DDT is highly persistent, with a soil half-life of 2-15 years and an aquatic half-life of about 150 years (NPIC 1999), it can pose a threat to bats when there is exposure to trace residues remaining in the environment (USGS 2013) or through bioaccumulation when quantities of contaminated insect prey are consumed. Extensive applications of insecticides and some bio control methods, such as Btk could also pose an indirect risk to red bats by reducing availability of insect prey.

Conservation Strategies and Management Practices

Research indicates that raising cut-in speeds (i.e., wind speed at which turbines first start rotating and generating electrical power) of wind turbines during peak migration times may limit the number of migratory tree bats killed (Baerwald et al. 2009; Arnett et al. 2011). Eastern red bats may roost in the remaining large trees in urban and agricultural areas and this can be important habitat to retain for them (Mager and Nelson 2001).

Research Needs

Research is needed to document specific roosting habitats in New York, and to determine population trends and regions of the state with the highest local abundances.



Eastern red bats most often roost among tree foliage or sometimes in shrubs, leaf litter, dense grass or under house shingles (Shump and Shump 1982; Mager and Nelson 2001). They may select roosting locations that are 1-12 m above the ground and shaded from above but open below (Saunders 1988). In urban or rural areas where woods have been cleared, large remaining trees may provide important roosting habitat (Mager and Nelson 2001). They use a variety of deciduous tree species for roosting; common ones in the Midwest include American elm (Ulmus americana), box elder (Acer negundo), sweetgum (Liquidambar syraciflua), and oaks (Quercus spp.) (Constantine 1966; Mager and Nelson 2001). On Long Island one was reported roosting on exposed roots on a beach cliff. Day roosts are frequently located in edge habitat along streams, open fields, near canopy gaps, or near urban areas (Constantine 1966; Mumford 1973; Shump and Shump 1982; Hutchinson and Lacki 2000), and are typically located within foraging areas (Elmore et al. 2005).

Eastern red bats may forage over open areas including over water, parks, pasture lands, along forest edges, in canopy gaps, and over clearcut harvests (Mager and Nelson 2001; Elmore et al. 2005; Walters et al. 2007). They are also known to forage around street lights and residential lighting that attract insects (Mager and Nelson 2001). They may select habitat at a landscape-level with a higher composition of water and moderate human development, and a lower composition of agriculture and dense forest (Mager and Nelson 2001; Loeb and O’Keefe 2006; Yates and Muzika 2006; Limpert et al. 2007; NYNHP unpubl. data).

Associated Ecological Communities

  • Allegheny oak forest (guide)
    A hardwood forest that occurs on well-drained sites in the unglaciated portion of southwestern New York. This is a forest of mixed oaks with a diverse canopy and richer ground flora than other oak communities in the state.
  • Appalachian oak-hickory forest (guide)
    A hardwood forest that occurs on well-drained sites, usually on ridgetops, upper slopes, or south- and west-facing slopes. The soils are usually loams or sandy loams. This is a broadly defined forest community with several regional and edaphic variants. The dominant trees include red oak, white oak, and/or black oak. Mixed with the oaks, usually at lower densities, are pignut, shagbark, and/or sweet pignut hickory.
  • Appalachian oak-pine forest (guide)
    A mixed forest that occurs on sandy soils, sandy ravines in pine barrens, or on slopes with rocky soils that are well-drained. The canopy is dominated by a mixture of oaks and pines.
  • Beech-maple mesic forest (guide)
    A hardwood forest with sugar maple and American beech codominant. This is a broadly defined community type with several variants. These forests occur on moist, well-drained, usually acid soils. Common associates are yellow birch, white ash, hop hornbeam, and red maple.
  • Coastal oak-beech forest (guide)
    A hardwood forest with oaks and American beech codominant that occurs in dry well-drained, loamy sand of morainal coves of the Atlantic Coastal Plain. Some occurrences are associated with maritime beech forest.
  • Coastal oak-heath forest (guide)
    A low diversity, large patch to matrix, hardwood forest that typically occurs on dry, well-drained, sandy soils of glacial outwash plains or moraines of the Atlantic Coastal Plain. The forest is usually codominated by two or more species of scarlet oak, white oak, and black oak.
  • Coastal oak-hickory forest (guide)
    A hardwood forest with oaks and hickories codominant that occurs in dry, well-drained, loamy sand of knolls, upper slopes, or south-facing slopes of glacial moraines of the Atlantic Coastal Plain.
  • Hemlock-northern hardwood forest (guide)
    A mixed forest that typically occurs on middle to lower slopes of ravines, on cool, mid-elevation slopes, and on moist, well-drained sites at the margins of swamps. Eastern hemlock is present and is often the most abundant tree in the forest.
  • Maple-basswood rich mesic forest (guide)
    A species rich hardwood forest that typically occurs on well-drained, moist soils of circumneutral pH. Rich herbs are predominant in the ground layer and are usually correlated with calcareous bedrock, although bedrock does not have to be exposed. The dominant trees are sugar maple, basswood, and white ash.
  • Oak openings (guide)
    A grass-savanna community that occurs on well-drained soils. In New York, these savannas originally occurred as openings within extensive oak-hickory forests. The best remnants occur on dolomite knobs.
  • Oak-tulip tree forest (guide)
    A hardwood forest that occurs on moist, well-drained sites in southeastern New York. The dominant trees include a mixture of five or more of the following: red oak, tulip tree, American beech, black birch, red maple, scarlet oak, black oak, and white oak.
  • Pitch pine-oak forest (guide)
    A mixed forest that typically occurs on well-drained, sandy soils of glacial outwash plains or moraines; it also occurs on thin, rocky soils of ridgetops. The dominant trees are pitch pine mixed with one or more of the following oaks: scarlet oak, white oak, red oak, or black oak.
  • Rich mesophytic forest (guide)
    A hardwood or mixed forest that resembles the mixed mesophytic forests of the Allegheny Plateau south of New York but is less diverse. It occurs on rich, fine-textured, well-drained soils that are favorable for the dominance of a wide variety of tree species. A canopy with a relatively large number of codominant trees characterizes this forest. Canopy codominants include five or more of the following species: red oak, red maple, white ash, American beech, sugar maple, black cherry, cucumber tree, and black birch.

Associated Species

  • Big Brown Bat (Eptesicus fuscus)
  • Hoary Bat (Lasiurus cinereus) (guide)
  • Little Brown Bat (Myotis lucifugus) (guide)
  • Northern Long-eared Bat (Myotis septentrionalis) (guide)


New York State Distribution

Eastern red bats occur throughout New York.

Global Distribution

The eastern red bat's summer range includes the central and eastern United States east of the Continental Divide, and southern Canada and northeastern Mexico (Baker et al. 1988; Cryan 2003; Reid 2006). There is evidence of skewed sex ratios in some regions but this appears to be at a local scale, unlike for hoary bats (L. cinereus) (Cryan 2003). The winter range of the eastern red bat is predominantly in the southeastern United States; however, they have been found farther north (Cryan 2003).

Identification Comments

General Description

Eastern red bats have red pelage that may appear brick to rusty red or buffy orange and is dense and wooly (Saunders 1988). The hair of the back and chest are tipped in white and they have a white shoulder patch. They have long, pointed wings and a long tail (Shump and Shump 1982). The bald parts of the tail and wing membranes are brownish black. Males tend to be more brightly colored than females and females are larger than males. Adults weigh 7-15 g (Shump and Shump 1982; Saunders 1988).

Identifying Characteristics

Eastern red bats can be distinguished from other New York species by their red fur. In flight, they can be distinguished by the position of their tail, which is extended straight out from the body (Shump and Shump 1982). They have a swift direct flight similar to hoary bats but they are much smaller.

Best Life Stage for Proper Identification

Adults and older juveniles may be easiest to identify.


Eastern red bats roost hanging upside down from one or both feet, and they often resemble a dead leaf hidden in tree foliage (Saunders 1988). Eastern red bats are solitary but may forage or migrate with other individuals (LaVal and LaVal 1979; Saunders 1988). Average home range sizes of 68 and 94 hectares have been reported (Elmore et al. 2005; Walters et al. 2007).

Pairs copulate while in the air and sometimes flutter to the ground (Saunders 1988). In some parts of their range, red bats swarm near cave entrances to mate, although they do not use the cave for winter shelters (Saunders 1988). Young are born in late June or July and there is some variation in the number of offspring produced ranging between 1 and 5, and averaging 2.3 (Hamilton and Stalling 1972; Mumford 1973; Shump and Shump 1982; Saunders 1988).

Red bats emerge from their roosts from 1-2 hours after sunset, which is later than for many species, but before hoary bats (Shump and Shump 1982). They exhibit a swift direct flight, although they may behave more erratically during foraging. They forage at multiple heights including high over forests and fields, and between the ground and canopy (Barbour and Davis 1969; Saunders 1988). They return to certain areas to forage nightly, typically within 300m of their day roosts (Saunders 1988). They are most active foraging during the few hours following sunset and before dawn (Shump and Shump 1982; Saunders 1988).

There is evidence to support the use of chemical signals to communicate in this species, such as the use of the same perch by different individuals in successive nights during migration (Saunders 1988). Eastern red bats are migratory and may typically move to southern states to overwinter where they probably hibernate in trees (Barbour and Davis 1969; Shump and Shump 1982).


A high percentage of the diet of the eastern red bat consists of beetles and moths with some regional differences in the variety of prey consumed. There are no known studies of diet in New York, however, there are several from the eastern United States. In South Carolina, eastern red bats consumed mostly beetles (Coleoptera) in early to mid summer but switched to a higher composition of moths (Lepidoptera) as beetle availability decreased in late summer (Carter et al. 2004). In West Virginia, eastern red bats preyed heavily on Lepidoptera which made up 47% of their diet followed by Coleoptera (25%), Tricoptera (10%), Homoptera (9%), and lesser amounts of Hemiptera, Diptera, and Hymenoptera (Carter et al. 2003). In southern Illinois, eastern red bats consumed primarily Lepidoptera (39%) followed by Homoptera (27%) and Coleoptera (23%), with lesser amounts of Diptera, Hemiptera, Hymenoptera, and Tricoptera (Feldhamer et al. 2009).

Best Time to See

The best time to see eastern red bats in New York is in late May through July in the early evening.  See Identification Characteristics for tips on distinguishing this species in flight.

  • Present
  • Reproducing

The time of year you would expect to find Eastern Red Bat present and reproducing in New York.

Eastern Red Bat Images


Eastern Red Bat
Lasiurus borealis (Muller, 1776)

  • Kingdom Animalia
    • Phylum Craniata
      • Class Mammalia (Mammals)
        • Order Chiroptera (Bats)
          • Family Vespertilionidae (Evening Bats and Vesper Bats)

Additional Resources


Arnett, E. B., M. M. P. Huso, M. R. Schirmacher and J. P. Hayes. 2011. Altering turbine speed reduces bat mortality at wind-energy facilities. Frontiers in Ecology & the Environment 9:209-214.

Arnett, E. B., W. K. Brown, W. P. Erickson, J. K. Fiedler, B. L. Hamilton, T. H. Henry, et al. 2008. Patterns of bat fatalities at wind energy facilities in North America. Journal of Wildlife Management 72:61-78.

Baerwald, E. F., Jason Edworthy, M. Holder and R. M. R. Barclay. 2009. A Large-Scale Mitigation Experiment to Reduce Bat Fatalities at Wind Energy Facilities. The Journal of Wildlife Management 73:1077-1081.

Baker, R. J., J. C. Patton, H. H. Genoways and J. W. Bickham. 1988. Genic studies of Lasiurus (Chiroptera: Vespertilionidae). Mammalogy Papers: University of Nebraska State Museum:97.

Barbour, R. W. and W. H. Davis [online]. 1969. Bats of America. University Press of Kentucky Lexington.

Carter, T. C., M. A. Menzel, B. R. Chapman and K. V. Miller. 2004. Partitioning of food resources by syntopic eastern red (Lasiurus borealis), Seminole (L. seminolus) and evening (Nycticeius humeralis) bats. The American midland naturalist 151:186-191.

Carter, T. C., M. A. Menzel, S. F. Owen, J. W. Edwards, J. M. Menzel and W. M. Ford. 2003. Food habits of seven species of bats in the Allegheny Plateau and ridge and valley of West Virginia. Northeastern Naturalist 10:83-88.

Childs, J. E., C. V. Trimarchi and J. W. Krebs. 1994. The Epidemiology of Bat Rabies in New York State, 1988-92. Epidemiology and Infection 113:501-511.

Constantine, D. G. 1966. Ecological observations on lasiurine bats in Iowa. Journal of Mammalogy 47:34-41.

Cryan, P. M. 2003. Seasonal distribution of migratory tree bats (Lasiurus and Lasionycteris) in North America. Journal of Mammalogy 84:579-593.

Elmore, L. W., D. A. Miller and F. J. Vilella. 2005. Foraging Area Size and Habitat Use by Red Bats (Lasiurus borealis) in an Intensively Managed Pine Landscape in Mississippi. The American Midland Naturalist 153:405-417.

Feldhamer, G. A., T. C. Carter and J. O. Whitaker. 2009. Prey Consumed by Eight Species of Insectivorous Bats from Southern Illinois. The American Midland Naturalist 162:43-51.

Hamilton, R. B. and D. T. Stalling. 1972. Lasiurus borealis with five young. Journal of Mammalogy:190-190.

Hutchinson, J. T. and M. J. Lacki. 2000. Selection of Day Roosts by Red Bats in Mixed Mesophytic Forests. The Journal of Wildlife Management 64:87-94.

LaVal, R. K. and M. L. LaVal. 1979. Notes on reproduction, behavior, and abundance of the red bat, Lasiurus borealis. Journal of Mammalogy:209-212.

Limpert, D. L., D. L. Birch, M. S. Scott, M. Andre and E. Gillam. 2007. Tree selection and landscape analysis of eastern red bat day roosts. Journal of Wildlife Management 71:478-486.

Loeb, S. C. and J. M. O'Keefe. 2006. Habitat Use by Forest Bats in South Carolina in Relation to Local, Stand, and Landscape Characteristics. Journal of Wildlife Management 70:1210-1218.

Mager, K. J. and T. A. Nelson. 2001. Roost-site Selection by Eastern Red Bats (Lasiurus borealis). The American Midland Naturalist 145:120-126.

Mumford, R. E. 1973. Natural history of red bat (Lasiurus borealis) in Indiana. Periodicum Biologorum 75:155-158.

National Pesticide Information Center (NPIC) [online]. 1999. DDT General Fact Sheet. <http://npic.orst.edu/factsheets/ddtgen.pdf> (18 November 2013).

New York Natural Heritage Program. 2019. New York Natural Heritage Program Databases. Albany, NY.

Reid, F. 2006. Peterson Field Guide to Mammals of North America: Fourth Edition. Houghton Mifflin Harcourt.

Saunders, D. A. [online]. 1988. Red Bat in Adirondack Mammals. State University of New York, College of Environmental Science and Forestry.

Shump, K. A. and A. U. Shump. 1982. Lasiurus borealis. Mammalian species:1-6.

U.S. Geological Survey [online]. 2013. House Bat Management Bat Toxicants. <http://www.npwrc.usgs.gov/resource/mammals/housebat/battox.htm> (18 November 2013).

Walters, B. L., C. M. Ritzi, D. W. Sparks and J. O. Whitaker Jr. 2007. Foraging behavior of eastern red bats (Lasiurus borealis) at an urban-rural interface. The American midland naturalist 157:365-373.

Whitaker, J. O. and L. R. Douglas. 2006. Bat Rabies in Indiana. Journal of Wildlife Management 70:1569-1573.

Winhold, L., A. Kurta and R. Foster. 2008. Long-term change in an assemblage of North American bats: are eastern red bats declining. Acta Chiropterologica 10:359-366.

Yates, M. and R. Muzika. 2006. Effect of forest structure and fragmentation on site occupancy of bat species in Missouri Ozark forests. Journal of Wildlife Management 70:1238-1248.

About This Guide

This guide was authored by: Kelly A. Perkins

Information for this guide was last updated on: March 25, 2014

Please cite this page as:
New York Natural Heritage Program. 2019. Online Conservation Guide for Lasiurus borealis. Available from: https://guides.nynhp.org/eastern-red-bat/. Accessed May 26, 2019.

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