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Demographics of a Barrier Island Box Turtle (Terrapene carolina) Population in a Relict Chenier Forest

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The animal most often associated with Louisiana, the American alligator, is but one among 147 amphibian and reptile species found in the state. From the ubiquitous green tree frog to the elusive slimy salamander, the variety of the state’s wildlife can be intriguing and overwhelming. In content that is both accessible to laypersons and relevant to herpetologists, Amphibians and Reptiles of Louisiana guides curious nature lovers and experienced biologists through a vast wealth of biodiversity. Jeff Boundy and John L. Carr describe the general form, sizes, and color patterns of each of Louisiana’s species: 23 salamanders, 30 frogs and toads, 26 turtles, 12 lizards, 47 snakes, and one alligator, along with eight non-native species now found in the state. Each entry considers the species’ behavior, geographic range, populations, food and feeding habits, reproduction, and predators. Useful identification keys to each genus are provided, while drawings of anatomical features, distribution maps, and color photographs serve as efficient visual aids. The authors offer techniques for locating amphibians and reptiles in their natural environments, as well as an illustrated summary of the landscape and habitats of Louisiana. Notation of endangered species and those of conservation concern is also included, along with a glossary and a list of additional references. With more than 780 color photographs and nearly 150 maps, this resource will enrich readers’ appreciation for Louisiana’s natural diversity and deepen their interest in the state’s complex ecology.
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We studied a population of ornate box turtles (Terrapene ornata) during 1977-87 in south-central Wisconsin, and intensively monitored (≥20 relocations) 53 radio-marked individuals during 1986-87. Egg laying occurred mainly in June; eggs in four nests hatched after 79-84 d. Twenty-one of 37 adult females (57%) laid during 1986-87, mean clutch size was 3.5, and hatchlings per adult female averaged 0.7. Mean annual survival of marked adults (age ≥10 yr) was 0.81 during 1977-87 (Jolly-Seber analysis). We estimated a total of 54-56 adults on four occupied sites within our 8 km2 study area. Adult densities at these sites ranged from 2.9-5.0/ha. Most (84%) turtles entered hibernation during Sept.; all emerged during April. Known periods of hibernation averaged 216 d (n = 9); burrow depths were between 0.5-1.8 m (n = 26). Mean home range size of adults was 8.7 ha (n = 47) annually, but varied greatly among individuals and did not differ significantly with sex or year. Home ranges of juveniles and subadults were much smaller. Areas of remnant prairie on deep sandy soil were frequented disproportionately, whereas agricultural cropland was clearly avoided. We compared demographic parameters of this and other turtle populations, and explored requisites for numerical stability with observed and hypothetical survival and recruitment rates. Our study area population will likely continue to decline because the average rate of adult survival (0.81 annually) is well below that (about 0.95) which would, with normal recruitment, stabilize numbers. Results of this study are discussed from a management perspective.
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The Lincoln-Petersen model (Chapter 2) and closed population models (Chapter 3) are presented briefly. The Jolly-Seber open population model is covered in detail in Chapter 4. In Chapter 5, the authors consider the "enumeration' or "calendar of captures' approach, which is widely used by mammalogists and other vertebrate ecologists, and recommend that it be abandoned in favor of analyses based on the Jolly-Seber model. One restricted version of the Jolly-Seber model, which allows losses (mortality or emigration) but not additions (births or immigration), is likely to be useful in practice. Another series of restrictive models requires the assumptions of a constant survival rate or a constant survival rate and a constant capture rate for the duration of the study. In Chapter 5, the authors consider 2 generalizations of the Jolly-Seber model. The temporary trap response model allows newly marked animals to have different survival and capture rates for 1 period. The other generalization is the cohort Jolly-Seber model. Ideally all animals would be marked as young, and age effects considered by using the Jolly-Seber model on each cohort separately. Chapter 6 presents a detailed description of an age-dependent Jolly-Seber model, which can be used when ≥2 identifiable age classes are marked. Detailed description of the "robust' design is given in Chapter 7, in which each primary period contains several secondary sampling periods. Chapter 8 gives detailed discussion of the design of capture-recapture studies. A new program has been written to accompany the material on the Jolly-Seber model (Chapter 4) and its extensions (Chapter 5). Another new program has been written for a special case of the age-dependent model (Chapter 6) where there are only 2 age classes. In Chapter 9 a description of the different versions of the 2 programs is given. Chapter 10 gives a description of some alternative approaches that were not considered in this monograph. -from Authors
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For decades conservation biologists have proposed general rules of thumb for minimum viable population size (MVP); typically, they range from hundreds to thousands of individuals. These rules have shifted conservation resources away from small and fragmented populations. We examined whether iteroparous, long‐lived species might constitute an exception to general MVP guidelines. On the basis of results from a 10‐year capture‐recapture study in eastern New York (U.S.A.), we developed a comprehensive demographic model for the globally threatened bog turtle (Glyptemys muhlenbergii), which is designated as endangered by the IUCN in 2011. We assessed population viability across a wide range of initial abundances and carrying capacities. Not accounting for inbreeding, our results suggest that bog turtle colonies with as few as 15 breeding females have >90% probability of persisting for >100 years, provided vital rates and environmental variance remain at currently estimated levels. On the basis of our results, we suggest that MVP thresholds may be 1–2 orders of magnitude too high for many long‐lived organisms. Consequently, protection of small and fragmented populations may constitute a viable conservation option for such species, especially in a regional or metapopulation context. Reexaminando el Concepto de Población Mínima Viable para Especies Longevas Resumen
Article
We studied a population of Florida Box Turtles, Terrapene carolina bauri, from September 2002 to December 2003, in the Florida Keys at the southernmost limit of its range. Population structure was estimated to be 7.5% juvenile, 58.75% female, and 33.75% male, resulting in a female biased sex ratio (1 male:1.74 females). Population size was estimated at 39.9–114.4 turtles/6 ha in a pine rockland forest, with an estimated density of 4.8–10.2 turtles/ha. Males had significantly longer carapace and plastron lengths than did females. Comparison of data with other populations of T. c. bauri revealed similar morphological characteristics among populations although this southern population had higher mean body mass than did populations in the central parts of its range.
Article
In the mid-Atlantic region, urban sprawl and development have resulted in habitat alterations and fragmentation; however, the effects on eastern box turtle (Terrapene carolina carolina) populations are unclear. To investigate the status of eastern box turtle populations in a fragmented landscape, we used mark—recapture and radiotelemetry to estimate population density, sex ratio, age structure, and survival on 4 study areas with differing degrees of isolation and human disturbance in northern New Castle County, Delaware, USA. We estimated adult population densities ranging from 0.81 turtles/ha to 3.62 turtles/ha among our 4 study areas. Sex ratios were male-biased at 2 study areas and balanced at 2 study areas. Proportion of juveniles ranged from 0% to 31%. Estimated annual survival rate ranged from 0.813 to 0.977. Mortality of radiotagged and marked turtles was primarily due to natural causes, but mowing was the primary cause of human-induced mortality. We found evidence of population decline at one study area due to low survival and recruitment. Human disturbances, isolation, and habitat composition appear to have the greatest influence on the box turtle populations we studied. To minimize mortality from human disturbance, we suggest planting crops adjacent to forest habitat that require no mowing or mowing at a height ≥15 cm. (JOURNAL OF WILDLIFE MANAGEMENT 72(3):745–753; 2008)
Article
A survey conducted in 1995 investigated long term declines reported in a population of box turtles Terrapene carolina monitored each decade since 1945 in bottomland hardwood forest at the Patuxent Wildlife Research Center, Maryland. Methods duplicated past surveys in most respects, but were supplemented by radiotelemetry and a survey of dominant vegetation. Seventy different turtles were found on the 11.8 ha study area, a decline of >75% since peak populations were recorded in 1955. Searchers were less efficient in 1995 than in 1945–1975 for a variety of possible reasons. Among turtles recorded, approximately equal numbers persisted from each of the past five decades, with some individuals surviving >70 years. A sex ratio strongly favoring males was first recorded in 1975 and continued in 1995, but juveniles and subadults were found in greater proportion in 1995 than in any other survey. Six of nine radio-marked turtles left the bottomland study area and migrated to the adjoining bluffs to hibernate, suggesting more extensive movements and perhaps less stable home ranges than formerly thought. Age structure of trees indicated a gradual change to more shade-tolerant species. Examination of rates of change from survey data suggested that major losses probably resulted from changes in hydrology that exacerbated flooding in 1972, with recovery only beginning in 1995 and perhaps limited both by repeated flood events and successional changes in the forest. Slow recovery from losses may indicate that populations of this species would respond poorly to exploitation. ©
Article
Using 28 topographic profiles, air-photo interpretation, and historical shoreline-change data, coastal processes were evaluated along the Chenier Plain to explain the occurrence, distribution, and geomorphic hierarchy of primary landforms, and existing hypotheses regarding Chenier-Plain evolution were reconsidered. The Chenier Plain of SW Louisiana, classified as a low-profile, microtidal, storm-dominated coast, is located west and downdrift of the Mississippi River deltaic plain. This Late-Holocene, marginal-deltaic environment is 200 km long and up to 30 km wide, and is composed primarily of mud deposits capped by marsh interspersed with thin sand- and shell-rich ridges (“cheniers”) that have elevations of up to 4 m.
Cheniere forest as stopover habitat for migrant landbirds: immediate effects of Hurricane Rita
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U.S. Dept. of Agriculture, Forest Service, Pacific Southwest Research Station, Albany, California. ---, p. chAdWicK, B. couviLLion, t. doyLe, s. FAuLKner, c. JesKe, t. Michot, L. rAndALL, c. WeLLs, And s. WiLson. 2007. Cheniere forest as stopover habitat for migrant landbirds: immediate effects of Hurricane Rita. U.S. Geological Survey 1306:147-156.
Guidelines for use of live amphibians and reptiles in field and laboratory research
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BeAupre, s. J., e. r. JAcoBson, h. B. LiLLyWhite, And K. zAMudio. 2004. Guidelines for use of live amphibians and reptiles in field and laboratory research. American Society of Ichthyologists and Herpetologists. Available at: http://www.asih.org/sites/default/files/ documents/resources/guidelinesherpsresearch2004.pdf. Accessed 21 Nov 2023.
A long-term study of eastern box turtles (Terrapene c. carolina) in a suburban neighborhood: survival characteristics and interactions with humans and conspecifics
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BrisBin, i. L., r. A. KennAMer, e. L. peters, And d. J. KArApAtAKis. 2008. A long-term study of eastern box turtles (Terrapene c. carolina) in a suburban neighborhood: survival characteristics and interactions with humans and conspecifics. Herpetol. Conserv. Bio. 3:367-380.
A. e. dunhAM, And r. c. vAn LoBen seLs. 1994. Demographics of common snapping turtles (Chelydra serpentina): implications for conservation and management of long-lived organisms
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conGdon, J. d. And J. W. GiBBons. 1990. The evolution of turtle life histories. In J. W. Gibbons (ed.), Life History and Ecology of the Slider Turtle, pp. 45-54. Smithsonian Institution Press, Washington, D.C. ---, A. e. dunhAM, And r. c. vAn LoBen seLs. 1994. Demographics of common snapping turtles (Chelydra serpentina): implications for conservation and management of long-lived organisms. Integr. Comp. Biol. 34:397-408.
Activity patterns and habitat use of box turtles (Terrapene carolina bauri) on a Florida island, with recommendations for management
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---And r. FrAnz. 1993. The need for status information on common herpetofaunal species. Herpetol. Rev. 24:47-49. ---And M. L. GriFFey. 2005. The conservation of box turtles on public lands in Florida. In W. E. Meshaka, Jr,. and K. J. Babbit (eds.), Amphibians and Reptiles: Status and Conservation in Florida, 1st ed., pp. 103-110. Krieger Publishing Company, Malabar, Florida. ---, r. FrAnz, And L. L. sMith. 1994. Activity patterns and habitat use of box turtles (Terrapene carolina bauri) on a Florida island, with recommendations for management. Chelonian Conserv. Biol. 1:97-106.
Leiden, s. poppy, and c. t. Winne. 2000. The global decline of reptiles
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giBBons, J. W., d. e. scott, t. J. ryAn, K. A. BuhLMAnn, t. d. tuBerviLLe, B. s. Metts, J. L. Greene, t. MiLLs, y. Leiden, s. poppy, and c. t. Winne. 2000. The global decline of reptiles, déjà vu amphibians. BioScience 50:653-666.
Louisiana Wildlife Action Plan. Louisiana Department of Wildlife and Fisheries
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hoLcoMB, s. r., A. A. BAss, c. s. reid, M. A. seyMour, n. F. Lorenz, B. B. GreGory, s. M. JAved, And K. F. BALKuM. 2015. Louisiana Wildlife Action Plan. Louisiana Department of Wildlife and Fisheries, Baton Rouge, Louisiana. xlii + 661 pp.
Terrapene carolina (Linnaeus 1758) -eastern box turtle, common box turtle
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Kiester, A. r., And L. L. WiLLey. 2015. Terrapene carolina (Linnaeus 1758) -eastern box turtle, common box turtle. Chelon. Res. Monogr. 5:1-25.
RMark: An R interface for analysis of capture-recapture data with MARK. AFSC Processed Rep. 2013-01. Alaska Fisheries Science Center
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LAAKe, J. L. 2013. RMark: An R interface for analysis of capture-recapture data with MARK. AFSC Processed Rep. 2013-01. Alaska Fisheries Science Center, NOAA, National Marine Fisheries Service, Seattle, Washington. 25 pp.
Louisiana Comprehensive Wildlife Conservation Strategy. Louisiana Department of Wildlife and Fisheries
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Lester, G., s. sorensen, p. FAuLKner, c. reid, And i. MAxit. 2005. Louisiana Comprehensive Wildlife Conservation Strategy. Louisiana Department of Wildlife and Fisheries, Baton Rouge, Louisiana. xx + 451 pp.