<<

Herpetology Notes, volume 14: 785-789 (2021) (published online on 18 May 2021)

Home-range size and activity of the Red-footed , carbonarius (Spix, 1824) in a Brazilian coastal shrub area

Patrícia Sayuri Shibuya1, Marcos Adriano Tortato¹, and Luiz Gustavo Rodrigues Oliveira Santos1,*

Abstract. movement studies may provide information for management. Here, we studied a population of Chelonoidis carbonarius in a natural environment using GPS devices. We tracked five individuals (one female and four males) in 2014 and the average home range size was 1.57 ± 1.15 ha, ranging from 0.29 ha to 3.09 ha. The individuals were active throughout the day, with no peak-activity.

Keywords. red-footed tortoise, movement, Testudinidae.

Introduction 2009; Noss et al., 2013). A review by Slavenko et al. (2016) showed that the home range of chelonians was Understanding animal movement patterns are essential not influenced by the sex and social structure. Only to shed light on several ecological processes related to body mass exerted some influence, however it explains an individual’s spatial requirements (Mace and Harvey, relatively little of the variation in home range size. 1983; Loehle, 1990). These studies are important because As are ectothermic they rely on environmental they can provide supporting information for species heat sources for their body temperature and this conservation and management actions (Türkozan et al., dependence may restrict their movements and daily 2018). Home range, as defined by Burt (1943), is the activities (Porter et al., 1973, Falcón et al., 2018). Most area covered by an individual during its normal activities tortoises are diurnal and their peak activity usually such as food gathering, mating, and caring for juveniles. occurs during the early morning and late afternoon (Rose Thenceforth, researchers are trying to understand which and Judd, 1975; Douglass and Layne, 1978; Lambert, factors determine an animal’s home range size and shape 1981; Mazzotti et al., 2002; McMaster and Downs, (Powell, 2000). Several factors may influence the home 2013). Some tortoises become inactive or lower their range size of an animal, such as age (Kleeberger and movements on hot days due to the risk of overheating Werner, 1982; Davis and Ford, 1983), sex (Brown and (Hailey et al., 1984, Hailey and Coulson 1996), but Orians, 1970; Barret, 1990), body size (Slavenko et al., daily activity rhythm is also highly variable between 2016), habitat quality (Simon, 1975; Ruby and Dunham, seasons (Geffen and Mendelssohn 1989; Mazzotti et al., 1987), season (Geffen and Mendelssohn, 1988; Brito, 2002; Rouag et al., 2017) 2003), and population density (Alberts, 1993). Tortoises are reported to have defined home ranges Study species.—Chelonoidis carbonarius (Spix, 1824) and one of the factors that might influence the size of is a medium-sized tortoise that ranges from south-eastern their home ranges is the season, since some species have Panama to Venezuela, Guyana, Suriname, , smaller home ranges during winter, when they are less , Peru, Bolivia, and Brazil (Rhodin et active (Eubanks et al., 2003; McMaster and Downs, al., 2017). This species is omnivorous and is influenced by the seasonal availability of food, consuming parts of such as flowers, and leaves, , vertebrates and fungi (Moskovits and Bjorndal, 1990; 1 Instituto de Biociências, Universidade Federal de Mato Grosso Jerozolimski et al., 2009; Wang et al., 2011). Females are do Sul, Rua UFMS, S/n - Cidade Universitária, Campo more active than males throughout the , especially Grande - MS, 79070-900, Brazil. during the non-breeding or nesting season (Moskovits * Corresponding author. E-mail: [email protected] and Kiester, 1987). Furthermore, C. carbonarius is © 2021 by Notes. Open Access by CC BY-NC-ND 4.0. more active during daylight, with a small increase in 786 Patrícia Sayuri Shibuya ����l.

the afternoon, especially in the rainy season (Noss et al., 2013). Here, for the first time, we deployed GPS devices on five Red-footed tortoises (Chelonoidis carbonarius) to provide descriptive information about home range size and activity of tortoises in a coastal shrub area in southern Brazil.

Material and methods Study Site. We conducted the study in a coastal area within Serra do Tabuleiro State Park located in southern Brazil (27°52’27” S, 48°49’26” O). This Park is inserted in the Atlantic Forest ecosystem and has several phytophysiognomies: ombrophilous forests, highlands, mangroves and coastal salt shrubs (IMA, 2019). We carried out the study in a coastal shrub area which is composed of sandy coastal strips covered by herbaceous and arbustive-arboreal vegetation (Suguio and Tessler, 1984; Araújo, 1992). Capture procedure and radio-tracking. In 2014 we captured tortoises through diurnal active searching. Once an individual was found, we weighed, sexed and identified it with epoxy numbers attached to its carapace. Sex was determined based on external characteristics (e.g. concavity of plastron and longer tails in males). All tortoises received unique-frequency GPS transmitters (Modified i-gotU® G120 GPS logger). Each transmitter weighed less than 3% of the tortoise’s body mass and was fixed to the tortoise’s carapace using epoxy glue. GPS transmitters were setup to record relocations every five minutes. Home-range estimation and activity. We used the package “adehabitatHR” (Calenge, 2006) to estimate home range size, using the 95% fixed kernel density estimator (KDE) method and 95% Minimum Convex Polygon (MCP). The activity pattern was calculated using the median of distance moved at each hour during all days of the monitoring period (June – October 2014).

Results We captured five adult : four males and one female. Body masses ranged from 3.51 kg to 4.80 kg (mean = 4.16 ± 0.52). The mean home range was 1.57 ± Figure 1. Home range, cumulative home range size and 1.15 ha: the largest and smallest estimated home ranges activity pattern of four male and one female adult Chelonoidis carbonarius in a coastal shrub area of southern Brazil. a) were both for males (3.09 ha and 0.29 ha, respectively) individual home ranges; b) cumulative home range; c) (Fig. 1A) (Tab. 1). Some home ranges have not activity; Dotted line: individual’s median of distance moved; stabilized yet which may lead to an underestimation of continuous line: population’s median of distance moved. home range size (Fig. 1B). Individuals showed uniform Home-range size and activity of the Red-footed Tortoise in Brazil 787 activities throughout the day (Fig. 1C), with no clear The tortoises monitored in our study did not follow activity peaks. the same activity patterns found in other studies, in which individuals were more active during the daylight Discussion throughout the year (Lambert, 1981; Mazzotti et al., 2002; McMaster and Downs, 2013; Rouag et al., 2017). Home range size estimated in our study (1.57± 1.15 ha) Although some studies showed some variations between was much smaller than other home range sizes reported sexes or seasons (Lambert, 1981; Mazzotti et al., 2002; in the literature: cocoa plantation (5.60±2.11 ha) (Borini McMaster and Downs, 2013; Rouag et al., 2017), they et al., 2014), Amazon (26.30±31.06 ha) (Moskovits do not apply to the results found in our study, since we and Kiester, 1987) and Chaco (124.47±177.18 ha) didn’t find the peak-activity of individuals. (Montaño et al., 2013). One of the factors that might One factor that can lead to a change in daily pattern have contributed to the variation in home range sizes activity is disturbance. The home ranges of our found in these studies compared to ours is the shorter study animals are close to the park headquarters, which monitoring time. In this study we monitored animals for is also very close to the city of Palhoça, state of Santa an average of 66 days, compared to the other studies (12 Catarina, Brazil. Some studies revealed the effect of months and 10 months) (Montaño et al., 2013; Borini on wildlife activity, which some species alter et al., 2014), with one exception (51 days in Moskovits daily activity and are becoming more nocturnal to avoid and Kiester, 1987). The shorter monitoring time may human disturbance (van Doormaal et al., 2015; Gaynor reflect an underestimation of home range size, because et al., 2018). Another reason possible explanation we can the areas may not have (Seaman et al., 1999; Girard et take into consideration is that the study site is not within al., 2002; Boyle et al., 2009). the original distribution range of the species (Rhodin et Although Moskovits and Kiester (1987) monitored al., 2017). This can lead to behavioural differences in individuals for an average of 51 days, specimens from the use of space (Frantzen et al., 2001; Nussear et al., there had larger home ranges. This could mean that the 2012), since temperature ranges and food availability animals in our study move less, and one of the factors are different, animal foraging strategies could change may be the environment. The coastal shrub vegetation is (Nagy and Medica, 1986; Peterson, 1996). strongly influenced by topography, which can have very This is the first study to use GPS transmitters to narrow (4 m) bands of elevations (sandy cords) and bands estimate home range size of the Red-footed tortoise. of depressions (inter-cords) (Araújo, 1992). Inter-coords Through the use of GPS, it is possible to obtain a large areas are subject to flooding, remaining flooded for at number of accurate locations per individual without least 6 months a year. Flooded areas might decrease the weather constraints (can be taken independently of area available for foraging (Crawshaw, 1991), leading season, weather, time of day) (Rodgers et al., 1996; to smaller home ranges than non-floodable areas (Bravo Dussault et al., 2000). Our results suggest that tortoises and Sallenave, 2003). We believe the inter-coords space in coastal areas had smaller home ranges than in other constrained tortoise’s activities to the very narrow sandy parts of their range and arrhythmic daily activity. coords or their edges. The elongated shape of home ranges also supports this idea, suggesting that tortoises were unable to cross the flooded inter-coords space.

Table 1. Identification number, sex, number of points and tracking days, and home-range size Table 1. Identification number, sex, number of points and tracking days, and home-range size of Chelonoidis carbonarius specimens ofsampled Chelonoidis in a coastal carbonarius shrub area specimens of southern sampled Brazil. in a coastal shrub area of southern Brazil.

ID Sex N. of Points N. of tracking days Kernel 95% (ha) MCP 95% (ha) J1 M 41196 139 0.80 3.31 J2 M 9906 37 0.29 0.28 J3 M 15219 54 1.28 2.06 J4 F 14441 28 2.43 1.89 J5 M 20388 74 3.09 5.80

1

788 Patrícia Sayuri Shibuya �� al.

References nocturnality. Science 360: 1232–1235. Geffen, E., Mendelssohm, H. (1988): Home range use and seasonal Alberts, A.C. (1993): Relationship of space use to population movements of the Egyptian tortoise ( kleinmanni) in the density in an herbivorous lizard. Herpetologica 49: 469–479. northwestern Negev, Israel. Herpetologica 44: 354–359. Araújo, D.S.D. (1992): Vegetation types of sandy coastal plains Geffen, E., Mendelssohn, H. (1989): Activity patterns and of Tropical Brazil: A first approximation. In: Coastal thermoregulatory behavior of the Egyptian tortoise Testudo communities of Latin America, p. 337–347. Seeliger, U., Ed, kleinmanni in Israel. Journal of Herpetology 23: 404–409. New York, USA, Academic Press. Girard, I., Ouellet, J.P., Courtois, R., Dussault, C., Breton, L. (2002). Barrett, S.L. (1990): Home range and habitat of the Effects of sampling effort based on GPS telemetry on home- (Xerobates agassizii) in the Picacho mountains of Arizona. range size estimations. The Journal of Wildlife Management 66: Herpetologica 46: 202–206. 1290–1300. Borini, J.F., Petrucci, B.B., Krohling, W., Rossi Junior, J.L., Santos, Hailey, A., Coulson, I.M. (1996): Temperature and the tropical M.R.D., Ferreira Junior, P.D. (2014): Site fidelity and movement tortoise spekii: constraints on activity level and body of Chelonoidis carbonaria (Spix, 1824) (Testudinidae) in cocoa temperature. Journal of Zoology 240: 523–536. plantations in southeastern Brazil. Brazilian Journal of Biology Hailey, A., Pulford, E.A., Stubbs, D. (1984): Summer activity 74: 135–141. patterns of Testudo hermanni Gmelin in Greece and France. Boyle, S.A., Lourenço, W.C., da Silva, L.R., Smith, A.T. (2009): Amphibia-Reptilia 5: 69–78. Home range estimates vary with sample size and methods. Folia IMA. Instituto do Meio Ambiente de Santa Cataria. (2019): Parque Primatologica 80: 33–42. Estadual da Serra do Tabuleiro. Available at: http://www.ima. Bravo, S.P., Sallenave, A. (2003): Foraging behaviour and activity sc.gov.br/index.php/ecosistemas/unidades-de-conservacao/ patterns of Alouatta caraya in the Northeastern Argentinean parque-estadual-da-serra-do-tabuleiro, accessed on 29th April flooded forest. International Journal of Primatology 24: 825– 2019. 846. Jerozolimski, A., Ribeiro, M.B.N., Martins, M. (2009): Are tortoises Brito, J.C. (2003): Seasonal variation in movements, home range, important seed dispersers in Amazonian forests? Oecologia 161: and habitat use by male Vipera latastei in northern Portugal. 517–528. Journal of Herpetology 37: 155–160. Kleeberger, S.R., Werner, J.K. (1982): Home range and homing Brown, J.L., Orians, G.H. (1970): Spacing patterns in mobile behavior of Plethodon cinereus in northern Michigan. Copeia animals. Annual Review of Ecology, , and 1982: 409–415. 1: 239–262. Lambert, M.R.K. (1981): Temperature, activity and field sighting Burt, W.H. (1943): Territoriality and home range concepts as in the Mediterranean spur-thighed or common garden tortoise applied to mammals. Journal of Mammalogy 24: 346–352. Testudo graeca L. Biological Conservation 21: 39–54. Calenge, C. (2006): The package adehabitat for the R software: Loehle, C. (1990): Home range: A fractal approach. Landscape a tool for the analysis of space and habitat use by animals. Ecology 5: 39–52. Ecological Modelling 197: 516–519. Mace, G.M., Harvey, P.H. (1983): Energetic constraints on home- Crawshaw, P.G. (1991): spacing, activity and habitat use in range size. The American Naturalist 121: 120–132. a seasonally flooded environment in Brazil. Journal of Zoology Mazzotti, S., Pisapia, A., Fasola, M. (2002): Activity and home 223: 357–370. range of Testudo hermanni in Northern Italy. Amphibia-Reptilia Davis, J., Ford, R.G. (1983): Home range in the western fence 23: 305–312. lizard (Sceloporus occidentalis). Copeia 1983: 933–940. McMaster, M.K., Downs, C.T. (2009): Home range and daily Douglass, J.F., Layne, J.N. (1978): Activity and movement of Leopard tortoises (Stigmochelys pardalis) in the of the ( polyphemus) in southern Nama-Karoo, South . Journal of Herpetology 43: 561– . Herpetologica 34: 359–374. 569. Dussault, C., Courtois, R., Ouellet, J.P., Huot, J. (2000): Evaluation McMaster, M.K., Downs, C.T. (2013): Seasonal and daily activity of GPS telemetry collar performance for habitat studies. Wildlife patterns of leopard tortoises (Stigmochelys pardalis Bell, 1828) Society Bulletin 27: 965–972. on farmland in the Nama-Karoo, South Africa. African Zoology Eubanks, J.O., Michener, W.K., Guyer, C. (2003): Patters of 48: 72–83. movement and burrow use in a population of gopher tortoises Montaño, R.R.F., Cuéllar, E., Fitzgerald, L.A., Soria, F., Mendonza, (Gopherus polyphemus). Herpetologica 59: 311–321. F., Peña, R., Dosapey, T., Deem, S.L., Noss, A.J. (2013): Ranging Falcón, W., Baxter, R.P., Furrer, S., Bauert, M., Hatt, J.M., Strub, patterns by the red-footed tortoise - carbonaria G.S., Ozgul, A., Bunbury, N., Clauss, M., Hansen, D.M. (2018): (Testudines: Testudinidae) - in the Bolivian Chaco. Ecología en Patterns of activity and body temperature of giant Bolivia 48: 17–30. tortoises in relation to environmental temperature. Ecology and Moskovits, D.K., Bjorndal, K.A. (1990): Diet and Food Preferences Evolution 8: 2108–2121. of the Tortoises Geochelone carbonaria and G. denticulata in Frantzen, M.A.J., Ferguson, J.W.H., de Villiers, M.S. (2001): The Northwestern Brazil. Herpetologica 46: 207–218. conservation role of captive African wild dogs (Lycaon pictus). Moskovits, D.K., Kiester, A.R. (1987): Activity levels and Biological Conservation 100: 253–260. ranging behaviour of the two Amazonian tortoises, Geochelone Gaynor, K.M., Hojnowski, C.E., Carter, N.H., Brashares, J.S. carbonaria and Geochelone denticulata, in North-Western (2018): The influence of human disturbance on wildlife Brazil. Functional Ecology 1: 203–214. Home-range size and activity of the Red-footed Tortoise in Brazil 789

Nagy, K.A., Medica, P.A. (1986): Physiological ecology of Desert Ruby, D.E., Dunham, A.E. (1987): Variation in home range size Tortoises in southern . Herpetologica 42: 73–92. along an elevational gradient in the iguanid lizard Sceloporus Noss, A.J., Montaño, F.R.R., Soria, F., Deem, S.L., Fiorello, C.V., merriami. Oecologia 71: 473–480. Fitzgerald, L.A. (2013): Chelonoidis carbonaria (Testudines: Seaman, D.E., Millspaugh, J.J., Kernohan, B.J., Brundige, G.C., Testudinidae) Activity Patterns and Burrow use in the Bolivian Raedeke, K.J., Gitzen, R.A. (1999): Effects of sample size Chaco. South American Journal of Herpetology 8: 19–28. on kernel home range estimates. The Journal of Wildlife Nussear, K.E., Tracy, C.R., Medica, P.A., Wilson, D.S., Marlow, Management 63: 739–747. R.W., Corn, P.S. (2012): Translocation as a conservation tool Simon, C.A. (1975): The influence of food abundance on territory for Agassiz’s desert tortoises: Survivorship, reproduction, and size in the iguanid lizard Sceloporus jarrovi. Ecology 56: 993– movements. The Journal of Wildlife Management 76: 1341– 998. 1353. Slavenko, A., Itescu, Y., Ihlow, F., Meiri, S. (2016): Home is where Peterson, C.C. (1996): Anhomeostasis: seasonal water and solute the shell is: predicting home range sizes. Journal of Animal relations in two populations of the Desert Tortoise (Gopherus Ecology 85: 106–114. agassizii) during chronic drought. Physiological Zoology 69: Suguio, K., Tessler, M.G. (1984): Planícies de cordões litorâneos 1324–1358. Quaternários do Brasil: Origem e nomenclatura. In: Restingas: Porter, W.P., Mitchell, J.W., Beckman, W.A., De Witt, C.B. (1973): origem, estrutura e processos, p. 32–56. Lacerda, L.D., Araújo, Behavioural implications of mechanistic ecology: thermal D.S.D., Cerqueira, R., Turq, B., Eds, Niterói, Brasil, Centro and behavioural modelling of desert ectotherms and their Editorial da Universidade Federal Fluminense. microenvironment. Oecologia 13: 1–54. Türkozan, O., Karaman, S., Yılmaz, C., Ülger, C. (2018): Daily Powell, R.A. (2000): Animal home range and territories and home movements and home range of Eastern Hermann’s Tortoise, range estimators. In: Research Techniques in Animal Ecology: Testudo hermanni boettgeri (Reptilia: Testudines). Zoology in Controversies and Consequences, p. 65–110. Boitani, L., Fuller, the Middle East 65: 28–34. T.K., Eds., New York, USA, Columbia University Press. van Doormaal, N., Ohashi, H., Koike, S., Kaji, K. (2015): Influence Rhodin, A.G.F., Iverson, J.B., Bour, R., Fritz, U., Georges, A., of human activities on the activity patterns of Japanese sika deer Shaffer, H.B., van Dijk, P.P. (2017). of the World (Cervus nippon) and wild boar (Sus scrofa) in Central Japan. – annotated checklist and atlas of , synonymy, European Journal of Wildlife Research 61: 517–527. distribution, and , Eighth edition. Chelonian Wang, E., Donatti, C.I., Ferreira, V.L., Raizer, J., Himmekstein, J. Research Monographs 7: 1–292. (2011): Food Habits and Notes on the Biology of Chelonoidis Rodgers, A.R., Rempel, R.S., Abraham, K.F. (1996): A GPS-based carbonaria (Spix 1824) (Testudinidae, Chelonia) in the Southern telemetry system. Wildlife Society Bulletin 24: 559–566. Pantanal, Brazil. South American Journal of Herpetology 6: Rose, F.L., Judd, F.W. (1975): Activity and home range size 11–19. of the tortoise, Gopherus berlandieri, in . Herpetologica 31: 448–456. Rouag, R., Ziane, N., Benyacoub, S. (2017): Activity patterns of the spur-thighed tortoise, Testudo graeca (Reptilia: Testudines: Testudinidae) in northeastern Algeria. Journal of Entomology and Zoology Studies 5: 177–180.

Accepted by Eric Munscher