Abstract
While the use of trees has been widely documented for most of the big cats, this information is scant for the jaguar (Panthera onca). In this study, we investigated the use of trees by jaguars, evaluating different underlying reasons as well as the frequency of tree use based on sex, age, and reproductive status. Data were obtained from 2013 to 2020 through a combination of direct observations during fieldwork and camera trapping focused on this behavior in the Brazilian Pantanal. We documented 252 climbing events (176 direct observations, 76 camera captures). Using only camera trapping data to avoid observers’ influence on jaguar behavior, we fitted generalized linear mixed models (GLMM) with jaguar identity as a random factor to test the effects of age, sex, and presence of conspecifics in the odds of animals climbing trees. We also used a generalized linear model (GLM) to test the effect of adult body weight on jaguar tree climbing probability. Age and presence of conspecifics were the most important drivers of jaguar climbing behavior in the study area, with cubs being more likely to climb trees than adults of either sex (odds ratio = 7.91, p < 0.001), and the presence of conspecifics, irrespective of age and sex, accentuated that behavior (odds ratio = 3.26, p < 0.005). Adult females (especially the lighter ones) and cubs were commonly recorded through direct observation on trees, a similar trend to our GLMM that showed a marginally negative effect of body weight on jaguar tree climbing probability. Only a few adult male jaguars ascended trees, and in all cases, these males were following females in heat. We suggest that trees are vertical extensions inside jaguar home ranges and may be safe refuges for resting and for protecting offspring against potential threats, including the harassment of large adult males.
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Introduction
Big cats can climb trees, and among large felid species, leopards (Panthera pardus) are most known to do so, hunting and managing to stash their prey on trees (Sunquist and Sunquist 2002). Selective pressure may have favored the development of this behavior in leopards because it minimizes kleptoparasitism by dominant competitors, such as lions (Panthera leo), hyenas (Crocuta crocuta), and tigers (Panthera tigris) (Stander et al. 1997; Karanth and Sunquist 2000; de Ruiter and Berger 2001). Leopards can also use trees as a refuge after being detected by competitors (Rafiq 2016) and for scent marking behaviors (Bothma and le Richet 1995). Cheetahs (Acinonyx jubatus), especially territorial males, use “play trees” for scent marking as part of their communications and territorial marking (Marker-Kraus et al. 1996). Serengeti lions climb trees to play, lie on the broad horizontal branches, scan the landscape looking for preys, or escape from harassment of buffalos (Syncerus caffer) and hyenas (Schaller 1972).
Although there are anecdotal reports about jaguars (Panthera onca) hiding in trees from hunters, little is known about tree use by the largest cat of the Neotropics throughout most of its range, with few previous records of tree use in threatening or stressful situations (Almeida 1990; Rampim et al. 2020). A recent study in a seasonally inundated island in the Amazon forest, however, has brought strong evidence of jaguars living an arboreal lifestyle during the three to 4-month-long wet season when the waters rise more than 10 m (Ramalho et al. 2021). In that region of the Amazon, the high canopy is the only dry ground available over ~ 11,000 km2 forcing jaguars to climb trees and prey chiefly on arboreal mammals such as brown-throated sloths (Bradypus variegatus) and red howler monkeys (Alouatta juara) (Rabelo et al. 2019). Unlike the extensive and continuous flooded forests present in large portions of the Amazon, the Pantanal biome is characterized by a mosaic landscape composed of open grasslands, marshes, savannas, and forests, presenting subtle differences in relief that regulate the flood during the 6-month-long wet season. Most tracts of forest stand higher than open habitats, and hence, the water level differs from around 1.5 m to as low as a few centimeters inside the forests (Gonçalves et al. 2011), which means that wildlife can still move widely around the landscape. In this seasonally flooded savannah, jaguars wander through both open and closed habitats all year round, and direct observations of jaguars climbing trees in our study area have raised some questions regarding factors that drive this behavior. Another striking distinction between Amazonian and Pantanal jaguars is related to their sizes, with the latter attaining much heavier body masses (Azevedo and Murray 2007; Ramalho et al. 2021).
Intraspecific killing (Azevedo et al. 2010) and infanticide (Soares et al. 2006; Tortato et al. 2017) may pose important threats to breeding females and their dependent young, forcing the need to find safe sites to increase survival chances of young until independence. For instance, female leopards can use abandoned aardvark (Orycteropus afer) burrows to protect their cubs (Steyn and Funston 2009). Female jaguars with cubs may shift their movement pattern to minimize the chance of encounters with potential infanticidal males, as hypothesized by Foster et al. (2010). In this scenario, trees may serve as safe shelter for the most vulnerable age-sex classes against the harassment and intraspecific killing by adult males, which are considerably larger than adult females throughout the species’ distribution (Seymour 1989) and may find more difficulties to climb and move on trees.
Here, we report the findings from the first systematic study of tree use by jaguars in the Brazilian Pantanal, the world’s largest freshwater wetland. We carried out surveys through field observations and camera trapping to (1) evaluate the frequency, activity patterns, and duration, (2) find the drivers associated with jaguar tree climbing behavior, and (3) better understand the individual characteristics of jaguars climbing trees (sex, age, and reproductive status). We used camera trap data and direct observations to test the hypothesis that in the Pantanal biome, trees may serve as safe refuges used by vulnerable sex-age classes to avoid harassment of large adult male jaguars. We expected to record cubs climbing trees more often than adults of either sex; adult males climb trees less frequently than adult females or cubs, and females with dependent young climb trees more often than lone adult females.
Methods
Study area
Caiman Ecological Refuge (CER) is located between the municipalities of Miranda and Aquidauana, Mato Grosso do Sul, Brazil, predominantly in the Pantanal but with some areas in Cerrado biome (Kanda et al. 2019). The landscape is composed of a mosaic of vegetation types, including exotic (e.g., perennial tropical grass Urochloa humidicola) and native pastures, dense forests, and patches of many different sizes of forest vegetation in a matrix of savannah grasslands. Much of the area is flooded during the rainy season (December–April). The CER is a ranch and nature reserve that stretches across ~ 530 km2 and has been raising cattle since 1916 and added wildlife tourism to the economic activities in 1987. Research and tourism focused on jaguars began in 2011. Previous studies have estimated a density of 6.5–7.0 jaguars per 100 km2 in the region (Soisalo and Cavalcanti 2006; Azevedo and Murray 2007).
Data collection
Direct observations
From 2013 to 2020, direct observations of jaguars using trees and additional information such as date, time, location, and tree species (if possible) were recorded. The direct observations occurred during (1) GPS monitoring and tracking of collared jaguars, (2) active search (e.g., following footprints and spotlighting), (3) tour activities with tourists, and (4) opportunistic encounters. Jaguars were identified to the individual level whenever possible, according to their unique rosette pattern.
Camera trapping
To evaluate if tree climbing is related to jaguar sex, age, and reproductive status, we monitored 18 trees using 36 trail cameras (Bushnell, Trophy Camera HD Brown–119876, Overland Park, Kansas, USA) from November 2018 through January 2020. Trees were selected based on previous sightings and/or signs of usage, such as claw marks, totalling five different tree species: fig tree (Ficus sp.), Tarumã tree (Vitex cymosa), pacara earpod tree (Enterolobium contortisiliquum), yellow trumpet tree (Tabebuia alba), and cabbage tree (Andira inermis). Half of the cameras were set on the ground, pointing in the direction of the trunk. The other half were attached to a main branch up in the tree (most likely to be used by jaguars) using a portable ladder with a maximum height of six meters (the chosen branches did not exceed this height) and climbing equipment. Cameras were deployed to record and individualize jaguars that could potentially climb trees, as well as to estimate the activity pattern and the duration that individual animals stayed on trees. The cameras were set to record 15 s at an interval of 0.6 s between recordings. They were checked every 2 months to download the recorded videos, change batteries, and assure proper functioning of the camera. All videos were stored in the project database, and the jaguars recorded were identified to the individual level. Five cameras were damaged by animals (e.g., cattle, capuchin monkeys, and woodcreepers) and three cameras burned during a fire in August 2019 that devastated around 300 km2 of the study area, causing the lack of data from two trees, which were removed from the analysis. The other cameras were replaced to continue the study.
We considered as a climbing event when the animal was recorded above the first trunk bifurcation and/or at the branches, considering independent events after 60 min of the previous one to avoid autocorrelation (Foster et al. 2013). If the same animal stayed up in the tree for more than 60 min, we considered it as a single event. The sex of individuals was recorded, and animals were classified as adults (independent from the mother) or cubs (animals still dependent on the mother’s care). Adult females were also classified in relation to their reproductive status as “mother” (with dependent cub) or “single” (no dependent cub) to test if the presence of cubs influences their climbing behavior. The presence of a conspecific (including cubs) was registered using binary code for “presence” and “absence” (1 and 0, respectively).
For 19 of the 37 individuals recorded in this study, we obtained exact weights after chemically restraining the animals for other scientific purposes not directly related with this study (e.g., biometry, collaring, and collecting biological samples). Then, we used this information to assess the effect of body mass on tree climbing behavior in jaguars (Online Resource 1 – Fig. S1).
Data analysis
To test the hypothesis that trees may serve as safe shelter against potential harassment of large adult males, we developed generalized linear mixed models (GLMM; Zuur et al. 2009) with a binomial distribution where independent climbing events detected by camera traps were the response variable and sex (i.e., male or female), age (i.e., adult or cub), and presence of conspecifics were the independent variables (Online Resource 1 – Table S1). Furthermore, to test whether females with dependent cubs were more likely to climb trees than females without cubs, we developed a GLMM using data only for climbing events of adult females using the presence of cubs as the moderator variable. For the purpose of these analysis, we chose the camera trap data to avoid any bias caused by the presence of observer as a factor to drive jaguars to climb trees. For controlling the possible effect of individual’s behaviors, the identity of jaguars entered the models as a random factor. We used Akaike’s information criteria controlled for small samples (AICC) to select the most parsimonious models (Burnham et al. 2011). To disentangle the effect of body weight and sex on jaguar climbing behavior, we have built a GLMM with a binomial distribution, including jaguar identity as a random effect, testing independent climbing events against body mass measured in kilogram. For this model, we have used only camera trap records of jaguars that we had exact data on body mass (n = 15). Furthermore, we also ran a generalized linear model (GLM) using the previous formulation without jaguar identity as a random factor, because we were expecting the loss of predictive power due to less degrees of freedom and fewer individuals with known weights (Online Resource 1 – Table S1, Fig. S1). All analyses were performed in R (R Core Team 2021), using the packages lmer (Bates et al. 2015) and AICcmodavg (Mazerolle 2020).
Results
Altogether, we observed a total of 252 independent tree climbing events, 176 detected by direct observations and 76 by camera traps (Table 1). Records of adult females with cubs represented 39.68%, followed by records of adult females without cubs (37.70%) and with cubs (20.64%). Only five records of adult male jaguars ascending trees were recorded in this study, representing only 1.98%.
Direct observations
From a total of 3,951 field observations, jaguars (three males and 15 females) were recorded ascending trees in 4.45% (n = 176) occasions on 144 different days. On four occasions, we observed adult males climbing trees; in three cases, they were following females to stay together with their mating pairs. In one case, a male that was tracking the odor of a female in heat climbed a tree, sniffed some branches for less than 3 min, and climbed down. Adult females (with and without cubs) were seen 155 times in trees. Although we did not carry out a systematic behavioral survey during the direct observations, we can state that most times (~ 80%) they were predominantly resting up in the trees. In eight, they were mobbed or ran away from white-lipped peccaries, and in three, they escaped from harassment of the cattle. In 15 events, females climbing trees were related to mating behavior, with males waiting under the trees in 11 cases. On two occasions, two different females were seen climbing trees in an attempt to catch coatis (Nasua nasua), a semi-arboreal prey. Regarding the females with cubs, on nine occasions, they were seen climbing trees accompanied by their offspring. Cubs were observed climbing trees 17 times, and on five occasions, they were without their mothers. Considering all jaguars recorded through direct observation, we found individual variation in the frequency of tree climbing behavior, with some individuals climbing trees more frequently than others (range = 1–125). One female jaguar accounted for 58.8% of all direct observations.
We identified jaguars climbing ten different tree species. Fig trees (Ficus sp.) and Tarumã (Vitex cymosa) represented 35.4% and 25% of the observations (when the tree species was known), with nine and eight jaguars climbing them, respectively (Table 2).
Camera trapping
Camera traps recorded 63,950 videos, 1,031 of jaguars (257.75 min). The 1,031 videos resulted in 76 independent records of individual jaguars climbing trees (Online Resource 1) and 168 independent records of jaguars not climbing. In total, 31 different individuals were filmed (20 females and 11 males). Twelve of them were recorded climbing trees, representing 45.7% (n = 471) of the videos. Eight adult females were recorded climbing trees in 40 events, while three cubs were filmed on trees in 35 occasions. There was only one record of an adult male climbing a tree (three sequential videos), sniffing the trunk and branches for more than 6 min. This event occurred 7 days after an adult female had climbed up the same tree for three consecutive days. Of the 76 tree climbing events, 44.7% took place between 05:00 and 09:59 h (Fig. 1), showing that jaguars climbed trees more often during the morning. In 73 events, it was possible to estimate the duration. Cubs and females with cubs spent longer times up in trees (Table 3). Among the 18 trees monitored with camera traps, five trees were not climbed by jaguars.
Models
Two of our GLMMs were equally plausible (ΔAICc < 2) and included age and presence of conspecifics as important moderators, and sex was also included by the top model (Online Resource 1 – Table S2), showing that age and presence of conspecifics are important drivers of climbing behavior of jaguars in the study area. Cubs are more likely to climb trees (odds ratio = 7.91, p < 0.001) than adults of either sex, while adult males are less likely to do so (odds ratio = 0.17, p = 0.08) compared to the other age-sex classes (Table 4, Online Resource 1 – Tables S2, S5 and S6). The presence of conspecifics, irrespective of age and sex, was also important and accentuated climbing behavior (odds ratio = 3.26, p < 0.005; Table 4, Online Resource 1 – Tables S2, S5 and S6). Looking only at adult females, the presence of cubs seems to influence their climbing behavior, but the difference was not significant (odds ratio = 2.49, p = 0.1, Table 5, Online Resource 1 – Tables S3 and S5). Regarding the effect of body weight on jaguar climbing behavior, our GLMM showed a marginally significant negative effect (p = 0.08), while the GLM detected a significant negative effect (Online Resource 1 – Fig. S2).
Discussion
To our knowledge this is the first study to systematically record tree climbing by jaguars in the Pantanal and to evaluate factors that favor this behavior. Considering the comparatively high number of records and the larger amount of time of mothers and cubs on trees, this behavior may be a strategy to increase the cubs’ survival during the first months of life. Infanticidal behavior by adult males has been previously reported for jaguar (Soares et al. 2006), as well as for other big cats, such as cougar (Puma concolor) (Logan and Sweanor 2001) and other Panthera species (e.g., tigers (Goodrich et al. 2008), lions (Schaller 1972; Pusey and Packer 1994), and leopards (Bailey 1993; Balme et al. 2013)). To deal with this potential threat, female jaguars can display mating behavior during cub rearing to minimize the chances of infanticide perpetrated by adult males (Fragoso et al. 2023). Therefore, use of trees as safer refuges to hide and protect vulnerable cubs from harassment and infanticide by adult males is an additional counterstrategy used by females. Trees could also protect the fragile cubs against other threats such as possible terrestrial predators or other aggressive species incapable to climb, such as white-lipped peccaries (e.g., Rampim et al. 2020). So, the learning process of the cubs may also be important for their own survival.
In 18 occasions, females were also recorded climbing up in the presence of their mates in an attempt to temporarily “escape” and rest, while the males usually waited under the trees or spent time marking the surrounding vegetation. This may indicate that the presence of a mate can be an influencing factor, prompting females to ascend trees, especially the heavier ones that are rarely recorded in other contexts. In our study, adult male jaguars climbed trees only on rare occasions, mostly in the pursuit of females for mating, suggesting that reproduction purposes may drive this behavior in males. Schaller (1972) observed that male lions in Serengeti ascended trees proportionally less often than females and cubs.
Although the GLM confirmed our hypothesis that body size is an important factor for the frequency of tree climbing, when the identity of jaguars was included in a GLMM, the effect became marginally significant. This is very likely due to the resulting reduction of degrees of freedom and for the fact that many individuals with known weight have few observations each. Three adult female jaguars ranging from 54 to 70 kg indeed were more likely to climb trees than any other jaguar, and they were responsible for 53% of the 129 observations. Adult male jaguars in our study area are significantly heavier than adult females (range = 102–140 kg and 51–100 kg, respectively), which means 36.5% of difference in mean weight. In this scenario, larger individuals are at higher risk of damaging from a tree fall, because some branches cannot resist their weight, so lighter individuals may be safe from predation when moving through branches where larger males cannot access without risking a fall. Indeed, there was only one observation of an adult male jaguar (107 kg) climbing a tree, which had been used a few days earlier by an adult female for consecutive days.
In a seasonally inundated forest in Amazon, both male and female jaguars adopt a semi-arboreal lifestyle, but in this area, adult female jaguars weighed 40–50 kg and males 50–60 kg (Ramalho et al. 2021), which are indeed in the lower range of adult weights for Pantanal jaguars. This is a morphological trace that would make it difficult for large Pantanal jaguars climb trees higher than 30 m as Amazon jaguars do (Ramalho et al. 2021). Furthermore, while the water column in the Amazon region reaches > 10 m in depth (Ramalho et al. 2009), in our study site, it reaches less than 0.5 m (Fragoso CE, personal observation), which means that wildlife can still move widely around the landscape, and hence, it is unlikely that the flood pulse is an important driver of jaguar tree climbing behavior in the Pantanal.
The adaptation to have a periodic arboreal and semiaquatic existence also depends on food resources during flood periods, and in Mamirauá, it is reported a high abundance of sloths and other arboreal mammals (Queiroz 1995), important prey for this big cat (Ramalho 2012). In our study area, there is no occurrence of sloths (Bradypus spp.), and there is a low availability of semi-arboreal prey species. As a consequence, arboreal and semi-arboreal prey species appear less important in jaguars’ diet, representing only 0.9% of coatis, 5% of southern tamanduas (Tamandua tetradactyla), and no primates (Fragoso CE, unpublished data). In the Pantanal, jaguars concentrate on caimans (Caiman yacare) and capybaras (Hydrochoerus hydrochaeris) as wild preys, which make up 45.8% and 14.8% of their diet at our study site, respectively (Fragoso CE, unpublished data).
Our results show that only one female accounted for more than half of the direct observations. But this specific jaguar is very habituated and easily located through the GPS/VHF collar, allowing long periods of direct observations and being one of the most seen individuals in the study site. This suggests that it is more related to an artifact of our visual monitoring than a specialization in tree climbing for some individuals.
The preference for fig trees and Tarumãs could be explained by the fact that both are common in the region, leafy, with many horizontal branches, providing shade, coverage, and comfortable places to rest. In addition, the structure of the fig trees (usually an unevenly growing trunk with ramifications that form low branches) can also facilitate the climbing of the cubs. Most of the Tarumã trees found in the study area are marked by clawing, probably because this species’ bark is soft, allowing jaguars to clean their claws while leaving a visual and olfactory marking.
Comparing our results with the available literature (Ramalho 2012; Ramalho et al. 2021), several variables may drive the tree climbing behavior in different places. This may be explained by the differences in the flood regimes, prey availability, body sizes, ecology, and evolution of the species to survive in areas under different conditions and landscapes. In addition to provide vegetation cover, an important environmental factor for this species (Morato et al. 2018), trees seem to be a vertical extensions of jaguars’ home ranges. Our findings show that in our study area, trees may act as safer places for the protection of more vulnerable age-sex classes against infanticide and harassment perpetrated by adult males and aggressive preys.
Data availability
All data analyzed during this study are included in this published article and its supplementary information files. Additional tables showing the distinct models, hypothesis, and predictions, as well as the model parameters, respective AICs, and model estimates, are presented in Online Resource 1. A compilation of camera trap videos is presented as Online Resource 2.
References
Almeida T (1990) Jaguar hunting in the Mato Grosso and Bolivia - with notes on other game. Safari Press, Long Beach, California
Azevedo FCC, Murray DL (2007) Spatial organization and food habits of jaguars (Panthera onca) in a floodplain forest. Biol Conserv 137(3):391–402. https://doi.org/10.1016/j.biocon.2007.02.022
Azevedo FCC et al (2010) Cannibalism among jaguars (Panthera onca). The Southwest Nat 55:597–599
Bailey TN (1993) The African leopard: ecology and behavior of a solitary felid. Columbia University Press, Ithaca, New York
Balme GA et al (2013) Reproductive success of female leopards Panthera pardus: the importance of top-down processes. Mammal Rev 43(3):221–237. https://doi.org/10.1111/j.1365-2907.2012.00219.x
Bates D et al (2015) Fitting linear mixed-effects models using lme4. J Stat Softw 67(1):1–48. https://doi.org/10.18637/jss.v067.i01
Bothma JDP, le Richet EAN (1995) Evidence of the use of rubbing, scent-marking and scratching-posts by Kalahari leopards. J Arid Environ 29:511–517. https://doi.org/10.1016/S0140-1963(95)80023-9
Burnham KP, Anderson DR, Huyvaert KP (2011) AIC model selection and multimodel inference in behavioural ecology: some background, observations, and comparisons. Behav Ecol Sociobiol 65:23–35. https://doi.org/10.1007/s00265-010-1029-6
de Ruiter DJ, Berger LR (2001) Leopard (Panthera pardus Linneaus) cave caching related to anti-theft behavior in the John Nash Nature Reserve, South Africa. Afr J Ecol 39(4):396–398. https://doi.org/10.1046/j.1365-2028.2001.00320.x
Foster VC et al (2013) Jaguar and puma activity patterns and predator-prey interactions in four Brazilian biomes. Biotropica 45(3):373–379. https://doi.org/10.1111/btp.12021
Foster RJ, Harmsen BJ, Doncaster CP (2010) Habitat use by sympatric jaguars and pumas across a gradient of human disturbance in Belize. Biotropica 42(6):724–731. https://doi.org/10.1111/j.1744-7429.2010.00641.x
Fragoso CE, Rampim LE, Quigley H, Haberfeld MB, Espíndola WA, Araújo VC, Sartorello LR, May-Júnior JA (2023) Unveiling demographic and mating strategies of Panthera onca in the Pantanal, Brazil. J Mammal 104(2):239–251. https://doi.org/10.1093/jmammal/gyac123
Gonçalves HC, Mercante MA, Santos ET (2011) Hydrological cycle. Braz J Biol 71:241–253. https://doi.org/10.1590/S1519-69842011000200003
Goodrich JM et al (2008) Survival rates and causes of mortality of Amur tigers on and near the Sikhote-Alin Biosphere Zapovednik. J Zool 276(4):323–329. https://doi.org/10.1111/j.1469-7998.2008.00458.x
Kanda CZ et al (2019) Spatiotemporal dynamics of conspecific movement explain a solitary carnivore’s space use. J Zool 308(1):66–74. https://doi.org/10.1111/jzo.12655
Karanth KU, Sunquist ME (2000) Behavioral correlates of predation by tiger (Panthera tigris), leopard (Panthera pardus) and dhole (Cuon alpinus) in Nagarahole. India J Zool 250(2):255–265. https://doi.org/10.1111/j.1469-7998.2000.tb01076.x
Logan KA, Sweanor LL (2001) Desert puma: evolutionary ecology and conservation of an enduring carnivore. Island Press, Washington DC
Marker-Kraus L, Kraus D, Barnett D, Hurlbut S (1996) Cheetah survival on Namibian farmlands. Cheetah Conservation Fund, Windhoek
Mazerolle MJ (2020) AICcmodavg: model selection and multimodel inference based on (Q)AIC(c). R package version 4.2.1
Morato RG et al (2018) Resource selection in an apex predator and variation in response to local landscape characteristics. Biol Conserv 228:233–240. https://doi.org/10.1016/j.biocon.2018.10.022
Pusey AE, Packer C (1994) Infanticide in lions: consequences and counterstrategies. In: Parmigiani S, vom Saal FS (eds) Infanticide and Parental Care. Harwood Academic Publishers, Chur, pp 277–299
Queiroz HL (1995) Preguiças e guaribas: os mamíferos folívoros arborícolas do Mamirauá. Sociedade Civil Mamirauá, Tefé, AM
R Core Team (2021) R: a language and environment for statistical computing. R Foundation for Statistical Computing, Vienna, Austria. https://www.R-project.org/
Rabelo RM, Aragón S, Bicca-Marques JC (2019) Prey abundance drives habitat occupancy by jaguars in Amazonian floodplain river islands. Acta Oecol 97:28–33. https://doi.org/10.1016/j.actao.2019.04.004
Rafiq K (2016) Risk-driven behavior in the African leopard: how is leopard behavior mediated by lion presence? Master thesis, Durham University
Ramalho EE (2012) Jaguar (Panthera onca) population dynamics, feeding ecology, human induced mortality, and conservation in the Várzea Floodplain Forests of Amazonia. Dissertation, University of Florida
Ramalho EE et al (2009) Ciclo hidrológico nos ambientes de várzea da Reserva de Desenvolvimento Sustentável Mamirauá-médio rio Solimões, período de 1990 a 2008. Uakari 5:61–87
Ramalho EE, Main MB, Alvarenga GC, Oliveira-Santos LGR (2021) Walking on water: the unexpected evolution of arboreal lifestyle in a large top predator in the Amazon flooded forests. Ecology 102(5):e03286. https://doi.org/10.1002/ecy.3286
Rampim LE, Sartorello LR, Fragoso CE, Haberfeld M, Devlin AL (2020) Antagonistic interactions between predator and prey: mobbing of jaguars (Panthera onca) by white-lipped peccaries (Tayassu pecari). Acta Ethol 23:45–48. https://doi.org/10.1007/s10211-020-00335-w
Schaller GB (1972) The Serengeti lion: a study of predator-prey relations. University of Chicago Press, Chicago
Seymour KL (1989) Panthera onca. Mamm Species 340:1–9
Sikes RS, Animal Care and Use Committee of the American Society of Mammalogists (2016) 2016 Guidelines of the American Society of Mammalogists for the use of wild mammals in research and education. J Mammal 97:663–688. https://doi.org/10.1093/jmammal/gyw078
Soares TN et al (2006) Paternity testing and behavioral ecology: a case study of jaguars (Panthera onca) in Emas National Park. Central Brazil Genet Mol Biol 29(4):735–740. https://doi.org/10.1590/S1415-47572006000400025
Soisalo MK, Cavalcanti SMC (2006) Estimating the density of a jaguar population in the Brazilian Pantanal using camera-traps and capture-recapture sampling in combination with GPS radio-telemetry. Biol Conserv 129(4):487–496. https://doi.org/10.1016/j.biocon.2005.11.023
Stander PE, Haden PJ, Kaqece II, Ghau II (1997) The ecology of asociality in Namibian leopards. J Zool 242(2):343–364. https://doi.org/10.1111/j.1469-7998.1997.tb05806.x
Steyn V, Funston PJ (2009) Land-use and socio-spatial organization of female leopards in a semi-arid wooded savanna, Botswana. S Afr J Wildl 39(2):126–132. https://doi.org/10.10520/EJC117324
Sunquist ME, Sunquist F (2002) Wild cats of the world. University of Chicago Press, Chicago, Illinois
Tortato FR et al (2017) Infanticide in a jaguar (Panthera onca) population—does the provision of livestock carcasses increase the risk? Acta Ethol 20:69–73. https://doi.org/10.1007/s10211-016-0241-4
Vitale A et al (2018) Guidelines for the treatment of animals in behavioral research and teaching. Anim Behav 135:1–10. https://doi.org/10.1016/j.anbehav.2019.11.002
Zuur AF et al (2009) Mixed effects models and extensions in ecology with R. Springer, New York
Acknowledgements
Special thanks are due to Caiman Pantanal for allowing this long-term jaguar conservation project, to Log Nature and Bushnell Corporation for the technical support in this study, to Onçafari team members (https://oncafari.org/), and to Érica Rosa for the help during the fieldwork. The authors also thank Arthur Fernandes and Wellyngton Espíndola Ayala for the statistical analysis, Peter Leimgruber and Ronaldo Gonçalves Morato for reviewing this paper, and Felipe Soares Bufalo for the first conversations about the analysis. HVBC has a scholarship granted by Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES), Brazil.
Funding
Our project was funded by the National Geographic Society, through the Early Career Grant (reference number EC-414R-18).
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Carlos Eduardo Fragoso: Conceptualization, methodology, formal analysis, investigation, resources, writing—original draft, writing—review and editing, funding acquisition.
Lilian Elaine Rampim: Methodology, investigation, writing—original draft, writing—review and editing.
Mario Haberfeld: Resources, writing—review and editing, funding acquisition.
Henrique Villas Boas Concone: Methodology, formal analysis, writing—review and editing.
Joares Adenilson May-Júnior: Methodology, writing—original draft, writing—review and editing.
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All the captured procedures followed the guidelines of American Society of Mammalogists (Sikes et al. 2016) and the guidelines for the treatment of animals in behavioral research (Vitale et al. 2018). All procedures were approved by the National Research Centre for Carnivores Conservation-ICMBio/CENAP, in Brazil (license numbers: SISBIO 30053–1, 30053–4, 30053–5, 30053–7, 30053–8, 61.844–2, 61.844–3, and 61.844–5).
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Fragoso, C.E., Rampim, L.E., Haberfeld, M. et al. Safe in the heights: trees as safer sites for female jaguars and their cubs in the Pantanal. acta ethol 26, 231–238 (2023). https://doi.org/10.1007/s10211-023-00425-5
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DOI: https://doi.org/10.1007/s10211-023-00425-5