Regular issues
Monographs
Special Issues



Southeastern Naturalist
    SENA Home
    Range and Scope
    Board of Editors
    Staff
    Editorial Workflow
    Publication Charges
    Subscriptions

Other EH Journals
    Northeastern Naturalist
    Caribbean Naturalist
    Neotropical Naturalist
    Urban Naturalist
    Eastern Paleontologist
    Journal of the North Atlantic
    Eastern Biologist

EH Natural History Home

Post-breeding Terrestrial Movements of Ambystoma tigrinum (Eastern Tiger Salamanders)
David A. Steen, Lora L. Smith, Gabriel J. Miller, and Sean C. Sterrett

Southeastern Naturalist, Volume 5, Number 2 (2006): 285–288

Full-text pdf (Accessible only to subscribers.To subscribe click here.)

 

Site by Bennett Web & Design Co.
2006 SOUTHEASTERN NATURALIST 5(2):285–288 Post-breeding Terrestrial Movements of Ambystoma tigrinum (Eastern Tiger Salamanders) David A. Steen1,*, Lora L. Smith1, Gabriel J. Miller1, and Sean C. Sterrett1 Abstract - To assess use of terrestrial habitat by ambystomatid salamanders, Ambystoma tigrinum (Tiger Salamanders) were monitored with radiotelemetry. Four individuals were tracked as they exited a wetland and made wide use of the surrounding landscape. Salamanders moved up to 255 m from the wetland of origin and found refugia both within forested land and wildlife food plots. Based on the extent of terrestrial movements by Tiger Salamanders, our findings support previous work demonstrating that upland habitat surrounding wetlands are critical areas in amphibian life cycles. Salamander movements did not appear to be influenced by agricultural development, as two individuals traveled through this habitat type. Introduction Ambystomatid salamanders make extensive use of terrestrial habitat surrounding breeding ponds (e.g., Douglas and Monroe 1981, Kleeberger and Werner 1983, Semlitsch 1981, Wacasey 1961, Williams 1973). For example, Semlitsch (1998) suggested a 164.3-m buffer surrounding wetlands would be necessary to protect 95% of individual ambystomatid salamanders in a breeding population, but data regarding movement patterns of several species were limited. Ambystoma tigrinum Green (Tiger Salamanders) are known to undertake considerable terrestrial movements (up to 286 m from wetlands, mean = 60.5; Madison and Farrand 1998) but scant information exists regarding movement of this species, particularly within the southern portion of its range (Semlitsch 1983). Study Area This study was conducted at the Joseph W. Jones Ecological Research Center at Ichauway (31o13'N, 84o29'W), an approximately 11,500-ha reserve. Ichauway is primarily a Pinus palustris Miller (longleaf pine) forest with undisturbed, native ground-cover species. The property is managed intensively with prescribed fire to maintain a pine/grassland community. Scattered individual hardwoods and hardwood patches exist within the longleaf pine matrix as a result of natural and manmade fire shadows. The site formerly was a private quail-hunting plantation, and portions of the site are still managed for traditional hunting, which has resulted in a diverse habitat mosaic of active and abandoned food plots within the forest matrix. 1Joseph W. Jones Ecological Research Center, Route 2, Box 2324, Newton GA, 39870. *Corresponding author - David.Steen@jonesctr.org. 286 Southeastern Naturalist Vol. 5, No. 2 Methods Herein we present data collected on four radio-tagged, post-breeding A. tigrinum exiting a 0.56 ha seasonally inundated wetland surrounded by predominantly mixed pine/hardwood forest. Approximately 40 m southwest of the wetland are 2 food plots (3.1 ha and 0.8 ha) bisected by a strip of mixed evergreen/deciduous hardwood forest (20 m x 400 m, 0.7 ha). Eight A. tigrinum (4 females and 4 males) were captured in pitfall traps at a drift fence as they exited the wetland between January–February 2005. Salamanders were anaesthetized by immersion in a 1:1000 solution of buffered MS-222 and surgically implanted with 0.8-g radio-transmitter units (BD-2H, Holohil Systems Ltd., Carp, ON, Canada) with an estimated battery life of 21 days. Surgical methods followed Madison (1997). After surgery, salamanders were held until a rain event (3–7 days) and released at dusk within 2 m of the trap where they were captured. The first 6 individuals were released on the same night in mid-January. Attempts to locate these individuals were undertaken after several hours, but their apparently extensive movements made locating them difficult. Two of these individuals were eventually located after a week of searching (female 3 and male 5; Table 1). Two additional animals were released, one in January and another in February, and were monitored every 30–60 minutes until movement ceased. Once an animal had found underground refugia and remained relatively stationary, it was monitored daily until battery failure or presumed predation. Results Prior to being located within a burrow, salamanders were observed crawling or stationary under leaf litter. Only one individual was found to use more than one burrow. When we discontinued monitoring, salamanders had not moved beyond their respective burrow for at least 2 days. There was considerable variability among individuals in total distance traveled and in total distance from the wetland (Table 1). Salamanders traveled overland relatively quickly; one individual (male 2) was found to have moved 28 m in 30 minutes and 17.9 m in 45 minutes Table 1. Movement data for four radio-tagged adult tiger salamanders (Ambystoma tigrinum). Total Total Total Straight line distance Sex ID Mass (g) fixesA locationsB movement (m)C from wetland (m)D Male 2 20.78 14 7 57.75 67.5 Female 3 13.22 3 1 235.80 255.5 Male 5 22.28 3 1 112.90 103.8 Male 6 20.65 14 4 27.40 15.9 ANumber of times an individual salamander was tracked and located. BNumber of unique locations where an individual was located. CTotal straight line distance between locations, commencing at release point. DStraight line distance from final location to closest wetland boundary. 2006 D.A. Steen, L.L. Smith, G.J. Miller, and S.C. Sterrett 287 between fixes. The transmitter from one salamander (male 6) was found 11 days after release at the mouth of a burrow in which the salamander had been residing for 3 days. The transmitter was etched and pitted, indicating that this was possibly a predation event. Two individuals were located only within the mixed pine/hardwood forest surrounding the wetland. However, one individual (male 2) was found within a wildlife food plot (3.1 ha), and another individual (female 3) was found within the strip of mixed evergreen/deciduous hardwood forest that was bordered on both sides by the food plots. Amphibian movements are known to be constrained by features of the landscape that disrupt forest connectivity (Gibbs 1998, Rothermel 2004). Interestingly, two of four A. tigrinum in our study traveled through or found refugia within wildlife food plots. In addition, the majority of salamanders captured at this wetland were caught in traps nearly adjacent to this land cover type (L.L. Smith, unpubl. data), suggesting that A. tigrinum may use this habitat extensively. Discussion Our results indicate adult A. tigrinum moved considerable distances— up to 255 m—from their breeding wetland, emphasizing the importance of upland habitat for pond-breeding salamanders. Although only four salamanders were successfully monitored with radio-transmitters, the study wetland contains a breeding population of several hundred individuals (L.L. Smith, unpubl. data). If movement data from this study are representative of the larger population, A. tigrinum appear to make wide use of the surrounding landscape, provided underground refugia are available. No evidence was gathered to suggest that A. tigrinum movements were constrained by agricultural development. Because of the relatively large number of burrowing rodents, e.g., Peromyscus polionotus Wagner (oldfield mice), that live in these areas, these habitats may actually provide increased opportunities for shelter. Small-mammal burrow density has been suggested as a potential factor limiting A. maculatum Shaw (Spotted Salamander) populations (Regosin et al. 2003). Additionally, food plots are tilled annually and the loose sandy soil may be particularly suitable for fossorial species such as A. tigrinum. Further research may reveal how agricultural development and altered small mammal populations may influence this species. Acknowledgments Thanks are extended to the Robert W. Woodruff Foundation for project support to the Joseph W. Jones Ecological Research Center at Ichauway. J.C. Brock provided assistance with GIS, E.P. Cox provided assistance obtaining references, and J.L. Gagnon provided comments on the manuscript. 288 Southeastern Naturalist Vol. 5, No. 2 Literature Cited Douglas, M.E., and B.L. Monroe. 1981. A comparative study of topographical orientation in Ambystoma (Amphibia: Caudata). Copeia 1981:460–463. Gibbs, J.P. 1998. Amphibian movements in response to forest edges, roads, and streambeds in southern New England. Journal of Wildlife Management 62:584–589. Kleeberger, S.R., and J.K. Werner. 1983. Post-breeding migration and summer movement of Ambystoma maculatum. Journal of Herpetology 17:176–177. Madison, D.M. 1997. The emigration of radio-implanted Spotted Salamanders, Ambystoma maculatum. Journal of Herpetology 31:542–551. Madison, D.M., and L. Farrand III. 1998. Habitat use during breeding and emigration in radio-implanted Tiger Salamanders, Ambystoma tigrinum. Copeia 1998:402–410. Regosin, J.V., B.S. Windmiller, and J.M. Reed. 2003. Influence of abundance of small-mammal burrows and conspecifics on the density and distribution of Spotted Salamanders (Ambystoma maculatum) in terrestrial habitats. Canadian Journal of Zoology 81:596–605. Rothermel, B.B. 2004. Migratory success of juveniles: A potential constraint on connectivity for pond-breeding amphibians. Ecological Applications 14:1535–1546. Semlitsch, R.D. 1981. Terrestrial activity and summer home range of the Mole Salamander (Ambystoma talpoideum). Canadian Journal of Zoology 59:315–322. Semlitsch, R.D. 1983. Terrestrial movements of an Eastern Tiger salamander, Ambystoma tigrinum. Herpetological Review 14:112–113. Semlitsch, R.D. 1998. Biological delineation of terrestrial buffer zones for pondbreeding salamanders. Conservation Biology 12:1113–1119. Wacasey, J.W. 1961. An ecological study of two sympatric species of salamanders, Ambystoma maculatum and Ambystoma jeffersonianum, in southern Michigan. Ph.D. Dissertation. Michigan State University, Lansing, MI. Williams, P.K. 1973. Seasonal movements and population dynamics of four sympatric Mole Salamanders, genus Ambystoma. Ph.D. Dissertation. Indiana University, Bloomington, IN.