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International Journal of
eISSN: 2574-9862

Avian & Wildlife Biology

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Received: January 01, 1970 | Published: ,

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Abstract

Little is known about clouded leopards (Neofelis nebulosa), who have a vulnerable population that extends across southern Asia. We reviewed the literature and synthesized what is known about their ecology and behavior. Much of the published literature either note detections within and on the edges of their range, or are anecdotal observations, many of which are decades if not over a century old. Clouded leopards are a medium-sized felid, with distinctive cloud-shape markings, and notably long canines relative to skull size. Estimates for population densities range from 0.58 to 6.53 individuals per 100km2. Only 7 clouded leopards have been tracked via radio-collars, and home range estimates range from 33.6-39.7km2 for females and 35.5-43.5km2 for males. Most accounts describe clouded leopards as nocturnal, but radio telemetry studies showed that clouded leopards have arrhythmic activity patterns, with highest activity in the morning followed by evening crepuscular hours. There has never been a targeted study of clouded leopard diet, but observations show that they consume a variety of animals, including ungulates, primates, and rodents. We encourage future study of their population density and range to inform conservation efforts, and ecological studies in order to understand the species and its ecological niche.

Keywords: activity patterns, clouded leopard, distribution, neofelis nebulosa, prey, population status

Abbreviations

SECR, spatially explicit capture recapture

Introduction

The global population of clouded leopards (Neofelis nebulosa) is considered vulnerable worldwide,1 and were considered to be less abundant globally the 2016 assessment by the IUCN than the previous assessment in 2007.1 Clouded leopards currently range from the southeastern Himalayas across southeastern Asia, extending through southern China and into peninsular Malaysia2-6 (Figure 1). They have been extirpated from Taiwan,7 and possibly from Bangladesh.1 Clouded leopards are protected in most countries across their range,1 but a large reason for population declines is unregulated hunting for pelts,1,8 as well as habitat fragmentation and regional declines in habitat quality.1

Figure 1 Distribution range (colored area) of clouded leopards, adapted from Grassman et al.1

Clouded leopards may be expanding their range recently in the southeastern Himalayas. Clouded leopards were historically found in Nepal,9 but were thought to have become extinct in the last century. They were rediscovered in the 1980’s,5 and have now been documented as far west as Annapurna in central Nepal.10 Similarly, clouded leopards were historically found in India and may have been common.11 They are now much less common, and were documented for the first time in decades in the northeastern state of Mizoram,12 and were also detected during multiple surveys during recent decades in the northeastern state of Arunachal Pradesh,13,14 and Assam.15 Future studies to document and confirm the global and local ranges of clouded leopards are important in order to set realistic and appropriate conservation goals. It is possible that the range is both expanding and contracting in different areas, making local conservation needs potentially different than those for the species as a whole. The expansions of the ranges of clouded leopards in the past few decades in Nepal and India,5,10,12-14 are encouraging. Although reintroductions are often difficult, because clouded leopards are naturally recolonizing areas it is possible that reintroduction efforts could also be successful. The causes of the original extirpation in the area need to be addressed and the long-term viability of the population considered before any reintroductions efforts begin.

Population densities and abundance

The population density estimates of clouded leopards range from 0.58 to 6.53 individuals per 100 km2 (Table 1). Advances in technology (i.e., motion-triggered cameras;)16 and statistical methods (i.e. n-mixture models,15 and spatially-explicit capture recapture [SECR] models,)17 make population densities easier to obtain in the past. As a result there has been a notable increase in the studies estimating clouded leopard population densities in the last decade. We strongly encourage this increase, with the goal of obtaining estimates of population densities across their entire range. This would allow researchers to understand baseline population densities in order to compare between populations, which is important for a species with vulnerable global status. These estimates can then be used to determine trends in population size and density over time. They can also be used to highlight areas of high conservation need, including where reintroductions may be feasible.

Study

Density

SE

Country

Statistical Method

Goswami & Ganesh

0.58

-

Assam, India

Relative Abundance Index

Borah et al.6

5.5

1.8

Assam, India

Jackknife Estimation in Capture

Borah et al.6

6.53

1.88

Assam, India

Pledger Models in Mark

Borah et al.6

4.73

1.43

Assam, India

Spatially-Explicit Capture Recapture

Mohamad et al.88

3.46

1

Peninsular Malaysia1

Spatially-Explicit Capture Recapture

Mohamad et al.88

1.83

0.61

Peninsular Malaysia2

Spatially-Explicit Capture Recapture

Table 1 The population density estimates available for clouded leopards from published literature, in number of individuals per 100 km2, and including their location and statistical method of estimation.

Due to their cryptic nature of clouded leopards have been notoriously difficult to document in the past, but the development of commercial camera traps has increased the ability for researchers to document clouded leopards (Table 2). Many of the past population estimates from camera data have large error values, however, and an area of research need is to determine methods of increasing accuracy. Methods of increasing detection rates, including the possible use of lures (e.g.,)18 and increasing the accuracy of the target locations should be considered. Another solution is to increase the density of cameras, along with possibly reducing the overall grid size, in order to increase the capture effectiveness. This may allow for greater capture and recapture of individuals, which would decrease the error values in population estimates. In SECR models, however, the maximum size between cameras should be the radius of a home range.17 The 2km distance used by Borah is well below the radius of known home ranges of clouded leopards (see below), although home range size could vary across their range. In conclusion, although camera density is important to consider, other methods to increase detection rates may be more important for decreasing the error estimates of population densities.

Study

Effort Days

Country

Datta et al.13

768

Arunachal Pradesh, India

Goswami & Ganesh

272.3

Assam, India

Mohamad et al. 88

128.8

Peninsular Malaysia1

Mohamad et al. 88

149.2

Peninsular Malaysia2

Moo et al.75

528.4

Myanmar

Ngoprasert et al.74

567.7

Thailand

Tan et al.75

173.2

Peninsular Malaysia

Tempa et al.94

113.1

Bhutan

Table 2 The camera trapping effort estimates available for clouded leopards from published literature with >3 photos, with effort estimates are in mean number of days for a capture.

Physical and genetic characteristics

Although belonging to Pantherinae, clouded leopards are a medium-sized felid, weighing between 11-23kg.4,19–21 They have distinctive large dark, cloud-shape markings, a tail typically as long as its head-body length (up to 80-90cm).19–22 Clouded leopards are notable for their relatively the long canine relative to skull size (3.8-4.5cm),3 the longest of living felids and reminiscent of saber-toothed tigers.23–24 Although the skull of clouded leopards does not reach pantherine size, it has attained pantherine cranial proportions (especially large teeth).25 Clouded leopards also have behavioral characteristics that fall between those of large and small felids.3,26 For example, similar to small felid species, they purr and cannot roar. Their method of eating food, grooming, and its body postures, however, are closer to those of the larger species of felids.26,27

Originally, clouded leopards were classified as a single member of the genus Neofelis28 that consisted of 4 subspecies.4 However, the latest genetic and morphometric research suggested that the former subspecies N.n. diardi in Sumatra and Borneo should be classified as a distinct species (i.e. N. diardi) based on distinct haplotypes,29 and pelage (smaller cloud markings, more cloud spots, and greyer fur).30 The Formosan clouded leopard (Neofelis nebulosa brachyurus) in Taiwan was first introduced to scientists by Swinhoe in 18622 and was described as a distinct species, Leopardus brachyurus, based on a shorter tail length.2 But,31 revised it to an insular race of the continental clouded leopards after acquiring more specimens.32,19 maintained that tail length is not a consistent criterion)33,34 even suggested that it is unnecessary to classify the Formosan clouded leopard as a distinct subspecies. Using samples from the National Taiwan Museum (7 specimen, but DNA was successfully extracted from only 1 sample), the latest genetic analysis showed that Taiwan clouded leopards diverged from the other mainland subspecies in haplotypes, but not to the level of a distinct species.29

Heterozygosity within clouded leopards has been examined in a population of 20 captive animals from USA zoos using allozymes only. The percent average heterozygosity (H) of clouded leopards was 2.3,35 which are similar to 2.3 for free ranging lions (Panthera leo) in Kruger National Park.36,37 However, clouded leopards had the fewest number of allozymes polymorphisms compared to 9 other felid species, with only the cheetah (Acinonyx jubatus) (a known bottleneck species) showing less heterozygosity.35,36 Further genetic work is needed to understand heterozygosity in given populations.

Home range and movement patterns

Over the last two decades researchers placed the first radio tracking collars on free-ranging clouded leopards.38,39 Tracked 2 adult clouded leopards in Thailand and reported that they occupied similarly sized home ranges (39.5km2 for 1 female and 42.2km2 for 1 male, 95% fixed kernel).39 Results in Thailand also showed no obvious differences of home range size (95% fixed kernel) between 2 adult males (35.5 and 43.5km2) and 2 adult females (33.6 and 39.7km2) in another area in Thailand. In addition, during camera trapping estimates from India individual clouded leopards were detected at cameras placed 2.0 to 13.6km apart. It is difficult to draw conclusions from such small sample sizes, but we note 2 observations of interest. First, the home range size of male and female clouded leopards appear to be similar in size, although male solitary felids tend to have notably larger home range sizes than females.40–44 Second, although there is a positive correlation between home range size and body size,45–47 the home range size reported for clouded leopards in Thailand38,39 are twice as large as male leopard (Panthera pardus) home ranges (18km2) reported elsewhere in Thailand.48 We are not sure if the reported home ranges are accurate for clouded leopards across their range, or if they are affected by local factors. A large variation in home range size has been observed in many solitary felid species, with a 10-fold variation in HRS common for species including bobcats (Lynx rufus),40 jaguars (Panthera onca),41,49,50 leopards51,42,44 and pumas (Puma concolor).43–52 Based on this potential variation, we do not know where the current estimates of clouded leopard home range size fall on the spectrum. Many of these studies have concluded that prey distribution and abundance, at least in part, is associated with home range size and population dynamics.40,44,50,53,54

Austin in 2002 tracked 2 radio-collared clouded leopards and reported that the female had a mean daily movement distance of 977m; the male had a mean daily movement distance of 1,168m, while Grassman39 reported an average 1,932m for 4 radio-tracked clouded leopards (range 122-7,724m). These are based on straight-line measurements and the distance moved could be higher when animals meandered between sampling locations. No dispersal data about clouded leopards are available. One subadult male clouded leopard was caught by local villagers in Nepal, and was then radio-collared and translocated 100km east of the original capture site.5 During the first 8 days of tracking it occupied an area less than 1km2, and then moved west toward where it was originally captured before the collar fell off after 10 days.5 Considering the large range of clouded leopards there are likely many factors that affect home range size, movement patterns, and dispersal. We are a proponent of non-invasive studies whenever possible, however, placing more radio-collars on clouded leopards across their range would increase our understanding of home range size and movement patterns. This would inform conservation efforts and likely also contribute to our understanding of other aspects of their ecology.

Reproductive and communication behavior

Reproductive and communication behavior is unknown in the wild for clouded leopards. A study of Sunda clouded leopard showed that they were similar to other felids (e.g.,)55,56 in using scent marking for intraspecific communication including territoriality, male-male competition, and mate selection.57 Sunda clouded leopards used 10 communication behaviors, including scraping, claw marking, urine spraying and cheek rubbing.57 Male Sunda clouded leopards ranged across larger areas, and overlapped at scent marking areas, while females did not.57

Clouded leopards are likely to exhibit reproductive and communication behaviors similar to other felids, especially Sunda clouded leopards and other species of the Panthera lineage Sensu.57 We encourage the use of motion-triggered cameras, which are a good method for documenting these behaviors and can be used across the range of clouded leopards. In captivity, clouded leopards begin breeding at 2 years old, and gestation lasts about 90 days.58 Clouded leopards can exhibit seasonality in breeding depending on length of day and light availability.58 Estrus lasts 3 to 6 days, and clouded leopards can exhibit spontaneous ovulation.58 Female clouded leopards exhibit increases in scent marking prior to estrus,58 which is similar to other solitary felids.59 Although studies in captivity inform our biological understanding, captivity also changes behavior,60,61 and understanding reproduction and communication behaviors in natural systems is an important area of research needed in the future.

Arboreal behavior

Clouded leopards have arboreal talents that rival those of the margay (Leopardus wiedi).4 Their relatively short, but powerful legs, large feet, and long tail are adaptations for arboreal life, giving clouded leopards a low center of gravity and a good grip on tree branches.21,62–64 In captivity, clouded leopards have been observed to climb about on horizontal branches with its back to the ground, and hang upside down from branches by its hind feet.65 Such behavior has been related to the hunting method of clouded leopards, in which they hang over tree branches and jump down upon passing prey.21 They have also been observed running down tree trunks headfirst in captivity,65 and was once observed in the wild hunting among a troop of pigtail macaques (Macaca nemestrina).66

Because of their arboreal talents, most literature describes clouded leopards as mainly arboreal based on local surveys and captive observations.20,21,67–71 Findings from studies using radio telemetry, however, suggested that clouded leopards may travel on the ground more often than in the trees.5,39,72 Contended that it could be difficult for clouded leopards to travel long distances through the trees. However, comparing the ratio of the sighting records in trees, clouded leopards are likely not primarily arboreal and instead uses trees as resting and hunting sites3,66,73 but variations may occur in different habitats or regions.

Habitat use

Early literature indicated that clouded leopards occurred in dense primary forests.19,20,67,68 Recent information, however, shows that clouded leopards are versatile and could occur in many different habitats. These habitats include: grassland,5 secondary or selectively logged forests,71 mature evergreen rain forests.71,74 These accounts however are opportunistic, and based on local interviews and records from hunting, tracks, and direct observations. Radio telemetry studies in Thailand showed variations in forest use comparing closed primary forest and more open secondary forest-grassland habitat.38,39 Three of the six clouded leopards tracked used vegetation types proportionally and two preferred closed primary forest. One occurred more in the open forest-grassland, which led39 to suggest that this particular clouded leopard used edges as hunting sites. Their results provided support for the generally held belief that clouded leopards occur in primary evergreen forest.4 Camera trapping in peninsular Malaysia has shown a preference in clouded leopards for forested habitats, and detections were more frequent with increasing distance from water bodies.75

Much of the literatures suggests that clouded leopards occur most often in lowlands.17,19,66,68,70 Other studies show that clouded leopards could occur as high as 2,585m in northeastern India,71 and clouded leopard detection at cameras was associated with higher elevations than lower elevation in Thailand.74 In peninsular Malaysia clouded leopard detections at cameras increased at higher elevations.75 However, occurrences of clouded leopards at these higher altitudes were extremely rare in the literature and were mostly indirect records based on interviews except a sighting by biologists at altitude 2,157m in northeastern India,12 and being found at nearly 3,000m in Nepal.10 Future studies of habitat based on explicit data are needed to understand the habitat clouded leopards are selecting for, and what drives this selection.74 Found that clouded leopard occurrence was linked to habitat used by red muntjac (Muntiacus muntjak) and Eurasian wild pigs (Sus scrofa), but further studies are needed to understand if habitat use is linked to habitat preferred by prey, or other factors such competition refuges from larger carnivores (e.g.,),76,15 and avoidance of people. Habitat use and elevation preferences are needed for setting realistic and effective conservation goals.

Activity patterns

Most accounts describe clouded leopards as nocturnal due to rare observation.2,19,21,68–70,77 Since clouded leopards have sometimes been seen traveling or hunting during daytime,66 they may not be as strictly nocturnal as previously assumed. Radio telemetry studies in Thailand showed that clouded leopards have arrhythmic activity patterns,38,39 with highest activity in the morning (801-1200) followed by evening crepuscular hours (1801-2000).39 Camera trapping in Thailand showed that 73% of observations were nocturnal.78 A future area of research is to determine the activity patterns of clouded leopards, if they vary in different areas, and if so, what causes the variation.

Two variables that may affect the activity patterns of clouded leopards are the activity patterns of prey and dominant carnivores.79 Proposed that predators track the activity periods of their prey, the activity patterns of felids, including ocelots (Leopardus pardalis), jaguars, and pumas, are related to those of their prey.80 Felids are also known to shift their temporal activity to avoid times when dominant carnivores are active, and in Thailand times of activity for clouded leopards most overlapped leopard cats (Prionailurus bengalensis) and tigers (Panthera tigris), with least overlap of leopards and marbled cats (Pardofelis marmorata).78 The use of radio tracking collars will be able to document activity patterns of clouded leopards, while the use of motion-triggered cameras could be used to determine activity patterns of clouded leopards as well as their prey and any dominant carnivores in the area.

Food habits

Like many other felids, clouded leopards consume a variety of animals, including ungulates, primates, rodents, domestic animals, and sometimes fish and snakes (Table 3). Our current understanding of clouded leopard diet is primarily from isolated observations, and is sure to be incomplete and not entirely accurate. For example, domestic animals are frequently reported, but this is likely because people are most likely to observe clouded leopards feeding on domestic animals. In contrast to Sunda clouded leopards, no birds have yet been noted in the diet of clouded leopards, but this is likely due to the very small sample of observations of clouded leopard prey to date. Also, although39 reported small mammals such as the Indochinese ground squirrel (Menetes berdmorei) and Muridae species in the diet, the stocky build, large canines and the large post canine space make clouded leopards capable of killing relatively large prey.19,21,81 It has historically been reported that clouded leopards will return to unfinished kills21,82,83 recently confirmed this by discovering a dead domestic goat cached on a tree branch 4m above the ground and saw a clouded leopard return to the kill the next day. Returning to feed on prey for multiple days until it is consumed is common in solitary felids (e.g.,42,52 especially when killing large prey that take multiple days to consume. Considering how important feeding ecology is to carnivores, remarkably little is known about the diet and feeding patterns of clouded leopards. We encourage future studies on the feeding ecology of clouded leopards, including diet composition, duration of feeding bouts, and how diet affects the energetic of clouded leopards. These studies could easily tie in with studies of activity patterns and how they are affected by prey species, how prey availability affects home range size, and how prey density affects the population densities of clouded leopards.

Source

Location

Type

Ungulates

Primates

Birds

Domestic

Rodent

Tickell [67]

India

Observation

No

No

No

Yes

No

Swinhoe2

Formosa

Observation

Yes

No

No

No

Brownlow

Tavoy

Observation

No

No

No

Yes

No

Editors

India

Observation

No

No

No

No

Yes

Davies66

Thailand

Observation

No

Yes

No

No

No

Hazarika

Assam

Observation

No

No

No

Yes

No

Grassman et al. 39

Thailand

Observation

Yes

No

No

No

No

Grassman et al. 39

Thailand

Scat/Trap

No

Yes

No

No

Yes

Table 3 The known prey items of clouded leopards. Studies are listed in chronological order, with their location, type of study, and whether the known frequent prey types were observed during the study. In the footnotes we list the known food items in as much detail as possible from the given study. Prey items. 1. Goats and Pigs, 2. Deer, 3. Cattle, 4. Porcupine, 5. Pig-Tailed Macaque (Macaca Nemestrina), 6. Goats, 7. Hog Deer (Axis porcine), 8. Malayan Pangolin (Manis javanica), 9. Slow Loris (Nycticebus coucang), 10. Bush tailed porcupine (Atherurus macrourus), 11. Indochinese ground squirrel (Menetes berdmorei).

Recommendations for future studies

The ecology and behavior of clouded leopards is relatively unknown when compared to other Panthera species. However, their populations are vulnerable world-wide,1 and are split into distinct sub-populations, many of which are declining.1 Considering their vulnerable status and their standing as a Panthera species, which are often flagship species for conservation,84 they are a species that needs more study. Many of the published studies about clouded leopards either a) note detections within and on the edges of their range, or b) are anecdotal studies recording observations, many of which are decades if not over a century old. Only 7 clouded leopards have ever had radio-collars placed on them, and these individuals are restricted to a small portion of the distribution of clouded leopards.85–92

Conclusion

Our areas of emphasis for future work include: 1) Population density and range. We consider an increased number of studies on clouded leopard population densities to be essential in future conservation of the species. The use of camera traps and new statistical methods appear to be good methods for estimating densities, and can be applied across their range. 2) Home range and movement. In order to understand clouded leopards we need to understand basic ecology, such as how much space they use, and understanding movement patterns will also be important for creation of corridors for conservation. 3) Ecological studies. There is much room for ecological studies, with recent studies have allowed us to remove folklore such as clouded leopards being primarily arboreal. However, little is still known about prey and hunting tactics, energetic, scent marking and communication, or interactions with other carnivores. Understanding these areas of clouded leopard natural history and ecology will help in creating effective conservation goals, and understanding the species and its ecological niche.

Acknowledgements

  1. European Commission - Environment - LIFE Programme
  2. The Spanish Ministry of Agriculture and Fish, Environment and Food
  3. Fundación Biodiversidad. España

Conflict of interest

The authors declare that there is no conflict of interests regarding the publication of this manuscript.

References

  1. Grassman L, Lynam A, Mohamad S, et al. Neofelis nebulosa. The IUCN Red List of Threatened Species. 2016.
  2. Swinhoe R. On the mammals of the island of Formosa. Proceedings of the Zoological Society of London. 1862;23:347–365.
  3. Guggisberg CAW. Wild cats of the world. 1st ed. USA: Taplinger Pub. Co; 1975.
  4. Nowell K, Jackson P. Wild cats: status survey and conservation action plan. Switzerland: IUCN, Gland; 1996.
  5. Dinerstein E, Mehta JN. The clouded leopard in Nepal. Oryx. 1989;23:199–201.
  6. Borah J, Sharma T, Das D, et al. Abundance and density estimates for common leopard Panthera pardus and clouded leopard Neofelis nebulosa in Manas National Park, Assam, India. Oryx. 2013;48:149–155.
  7. Chiang CE, Wang TD, Ueng KC, et al. Guidelines of the Taiwan Society of Cardiology and the Taiwan Hypertension Society for the management of hypertension. J Chin Med Assoc. 2015;78(1):1–47.
  8. Cruze ND, Macdonald DW. Clouded in mystery: the global trade in clouded leopards. Biodiversity and Conservation. 2015;24(14):3505–3526.
  9. Hodgson BH. Felis macrosceloides. Proceedings of the Zoological Society of London. 1853:21–23.
  10. Ghimirey Y, Acharya R, Adhikary B, et al. Clouded leopard camera–trapped in the Annapurna Conservation Area, Nepal. Cat News. 2013;58:25.
  11. Jerdon TC. The mammals of India: a natural history of all the animals known to inhabit continental India. London: London J Wheldon Publisher; 1874.
  12. Ghose D. First sighting of clouded leopard Neofelis nebulosa from the Blue Mountain National Park, Mizoram, India. Current Science. 2002;83(1):20–21.
  13. Datta A, Anand MO, Naniwadekar R. Empty forests: Large carnivore and prey abundance in Namdapha National Park, north–east India. Biological Conservation. 2008;141:1429–1435.
  14. Velho N, Srinivasan U, Singh P, et al. Large mammal use of protected and community‐managed lands in a biodiversity hotspot. Animal Conservation. 2016;19:199–208.
  15. Royle JA. N–mixture models for estimating population size from spatially replicated counts. Biometrics. 2004;60(1):108–115.
  16. Burton AC, Neilson E, Moreira D, et al. Wildlife camera trapping: A review and recommendations for linking surveys to ecological processes. Journal of Applied Ecology. 2015;52:675–685.
  17. Royle J, Richard B Chandler, Rahel Sollmann, et al. Spatial capture–recapture. USA: Academic Press; 2013.
  18. Tanner D, Zimmerman P. Optimal attractants to increase visits by clouded leopards to remote‐camera sets. Wildlife Society Bulletin. 2012;36(3):594–599.
  19. Pocock RI. The fauna of British India. 2nd ed. London: Taylor and Francis; 1939.
  20. Prater SH. The book of Indian animals. 2nd ed. Bombay Natural History Society: Prince of Wales Museum of Western India. India; 1965.
  21. Lekagul B, MacNeely JA, Marshall JT, et al. Mammals of Thailand. Thailand: Sahakarnbhat; 1977.
  22. Metha JN, Dhewaju RG. A note on the record of clouded leopards in Nepal. AGRIS. 1990;17:21–22.
  23. Sterndale RA. Natural history of the mammalia of India and Ceylon. India: Himalayan Books; 1884.
  24. Christiansen P. Sabertooth characters in the clouded leopard (Neofelis nebulosa Griffiths 1821). J Morphol. 2006;267(10):1186–1198.
  25. Werdelin L. Morphological patterns in the skulls of cats. Biological Journal of the Linnean Society. 1983;19(4):375–391.
  26. Gao YT. Fauna Sinica, Mammalia, Vol. 8: Carnivora. China: Science Press; 1987.
  27. Mellen JD. Little–known cats, Great cats: majestic creatures of the wild. In: Seidensticker J, Lumpkin S, et al. editors. USA: Rodale Press; 1991. p. 170–179.
  28. Ewer RF. The carnivores. USA: Comstock Pub Associates; 1973.
  29. Buckley Beason VA, Johnson WE, Nash WG, et al. Molecular evidence for species–level distinctions in clouded leopards. Curr Biol. 2006;16(23):2371–2376.
  30. Kitchener AC, Beaumont MA, Richardson D. Geographical variation in the clouded leopard, Neofelis nebulosa, reveals two species. Curr Biol. 2006;16(23):2377–2383.
  31. Swinhoe R. Catalogue of the mammals of China (south of the river Yangtsze) and the island of Formosa. Proceedings of the Zoological Society of London. 1870;32:615–653.
  32. Horikawa Y. Survey of Formosan mammals (IV). Transactions of the Natural History Society of Formosa. 1930;20:277–284.
  33. Kuroda N. Checklist to the mammals of Japan. Japan; 1938.
  34. Kuroda N. A monograph of the Japanese mammals. Japan: The Sanseido Co. Ltd; 1940.
  35. Wang Y, Chu S, Wildt D, et al. Clouded leopard–Taiwan (Neofelis nebulosa brachyurus) Population and Habitat Viability Assessment. IUCN/SSC Conservation Breeding Specialist Group. 1995.
  36. Newman A, Bush M, Wildt DE, et al. Biochemical genetic variation in 8 endangered or threatened felid species. Journal of Mammalogy. 1985;66:256–267.
  37. Miththapala S, Seidensticker J, Phillips LG, et al. Genetic variation in Sri–Lankan leopards. Zoo Biology. 1991;10:139–146.
  38. Austin SC. Ecology of sympatric carnivores in Khao Yai National Park, Thailand. The university of Hong Kong Libraries; 2003.
  39. Grassman LI, Tewes ME, Silvy NJ, et al. Ecology of three sympatric felids in a mixed evergreen forest in north–central Thailand. Journal of Mammalogy. 2005;86:29–38.
  40. Bailey TN. Social organization in a bobcat population. JSTOR. 1974;38(3):435–446.
  41. Schaller GB, Crawshaw PG. Movement patterns of jaguar. JSTOR. 1980;12(3):161–168.
  42. Bailey TN. The African leopard: ecology and behavior of a solitary felid. The university of Chicago press journals. 1993:69(4).
  43. Brian R, Spreadbury RR, Kevin Musil, et al. Cougar population characteristics in southeastern British Columbia. JSTOR. 1996;60(4):962–969.
  44. Mizutani F, Jewell PA. Home–range and movements of leopards (Panthera pardus) on a livestock ranch in Kenya. AGRIS. 1998;244:269–286.
  45. Harestad AS, Bunnell FL. Home range and body weight – re–evaluation. Ecology. 1979;60(2):389–402.
  46. Gittleman JL, Harvey PH. Carnivore home–range size, metabolic needs and ecology. JSTOR. 1982;10(1):57–63.
  47. Mace GM, Harvey PH, Clutton Brock TH. Vertebrate home–range size and energetic requirements. In: Swingland IR, Greenwood PJ, editors. The ecology of animal movement. UK: Clarendon Press; 1983. p. 32–53.
  48. Grassman LI. Ecology and behavior of the Indochinese leopard in Kaeng Krachan National Park, Thailand. Natural History Bulletin of the Siam Society. 1999;47:77–93.
  49. Rabinowitz AR, Nottingham BG. Ecology and behavior of the jaguar (Panthera onca) in Belize, Central–America. Journal of Zoology. 1986;210:149–159.
  50. Crawshaw PG, Quigley HB. Jaguar spacing, activity and habitat use in a seasonally flooded environment in Brazil. Journal of Zoology. 1991;223:357–370.
  51. Bertram BCR. Leopard ecology as studies by radio tracking. SSC. 1982;49:341–352.
  52. Elbroch LM, Lendrum P, Allen ML, et al. Nowhere to hide: pumas, black bears, and competition refuges. Behavioral Ecology. 2015;26(1):247–254.
  53. Seidensticker J. On the ecological separation between tigers and leopards. JSTOR. 1976;8(4):225–234.
  54. Emmons LH. A field study of ocelots (Felis pardalis) in Peru. Revue D Ecologie. 1988;43:133–157.
  55. Smith JLD, McDougal C, Miquelle D. Scent marking in free–ranging tigers, Panthera tigris. Animal Behavior. 1989;37:1–10.
  56. Allen ML, Hocevar L, Krofel M. Where to leave a message? The selection and adaptive significance of scent–marking sites for Eurasian lynx. Behavioral Ecology and Sociobiology. 2017;71:136.
  57. Maximilian L Allen, Heiko U Wittmer, Endro Setiawan, et al. Scent marking in Sunda clouded leopards (Neofelis diardi): novel observations close a key gap in understanding felid communication behaviours. Sci Rep. 2016;6:35433.
  58. Brown JL. Female reproductive cycles of wild female felids. Animal Reproduction Science. 2011;124(3):155–162.
  59. Allen ML, Wittmer HU, Houghtaling P, et al. The role of scent marking in mate selection by female pumas (Puma concolor). PLoS One. 2015;10:e0139087.
  60. Mallapur A, Chellam R. Environmental influences on stereotypy and the activity budget of Indian leopards (Panthera pardus) in four zoos in southern India. Zoo Biology. 2002;21:585–595.
  61. Quirke T, O Riordan RM, Zuur A. Factors influencing the prevalence of stereotypical behaviour in captive cheetahs (Acinonyx jubatus). AGRIS. 2012;142:189–197.
  62. Gonyea WJ. Adaptive differences in the body proportions of large felids. Acta Anat (Basel). 1976;96(1):81–96.
  63. Gonyea WJ. Functional Implications of felid forelimb anatomy. Acta Anatomica. 1978;102:111–121.
  64. Taylor ME. Locomotor adaptions by carnivores. In: Gittleman JLE, editor. Carnivore behavior, ecology, and evolution. Greece: Comstock; 1989. p. 382–409.
  65. Hemmer H. Untreated by the Pantherkatzen (Pantherinae) II: Studien zur ethologie des Nebelparders Neofelis nebulosa (Griffith 1821) and Irbis Uncia uncia (Schreber 1775). [Studies of the phylogenetic history of the Pantherina II: Research into the ecology of the clouded leopard and snow leopard.]. Veröffentlichungen der Zoologischen Staatssammlung München. 1968;12:155–247.
  66. Davies RG. Sighting of a clouded leopard (Neofelis nebulosa) in a troop of pigtail macaques (Macaca nemestrina) in Khao Yai National Park, Thailand. Siam Society Natural History Bulletin. 1990;38:95–96.
  67. Tickell SR. Notes on a curious species of tiger or jaguar, killed near the Snowy Range, north of Darjeeling. Journal of the Asiatic Society of Bengal. 1843;12:814–816.
  68. Renshaw G. More natural history essays. London: Sherratt and Hughes; 1905.
  69. Humphrey SR, Bain JR. Endangered animals of Thailand. USA: Sandhill Crane Press; 1990.
  70. Choudhury A. The clouded leopard in Assam. Oryx. 1993;27(1):51–53.
  71. Choudhury A. The clouded leopard in Manipur and Nagaland. Journal of the Bombay Natural History Society. 1997;94:389–391.
  72. Austin SC, Tewes ME. Ecology of the clouded leopard in Khao Yai National Park, Thailand. Cat News. 1999;31:17–18.
  73. Lloyd E, Kreeltiyutanont K, Prabnasuk J, et al. Observation of Phayre's leaf monkeys mobbing a clouded leopard at Phu Khieo Wildlife Sanctuary (Thailand). Mammalia. 2006;70(12):158–159.
  74. Ngoprasert D, Lynam AJ, Sukmasuang R, et al. Occurrence of three felids across a network of protected areas in Thailand: prey, intraguild, and habitat associations. Biotropica. 2012:1–8.
  75. Tan CKW, Rocha DG, Clements GR, et al. Habitat use and predicted range for the mainland clouded leopard Neofelis nebulosa in Peninsular Malaysia. Biological Conservation. 2017;206:65–74.
  76. Durant SM. Competition refuges and coexistence: an example from Serengeti carnivores. JSTOR. 1998;67(3):370–386.
  77. Kanchanasakha B, Simcharoen S, Than UT. Carnivores of mainland South–East Asia. 1st ed. Bangkok: WWF; 1998.
  78. Lynam AJ, Jenks KE, Tantipisanuh N, et al. Terrestrial activity patterns of wild cats from camera–trapping. Raffles Bulleting of Zoology. 2013;61:407–415.
  79. Curio E. The ethology of predation. New York; 1976.
  80. Emmons LH. Comparative feeding ecology of felids in a neotropical rainforest. JSTOR. 1987;20(4):271–283.
  81. Therrien F. Feeding behaviour and bite force of sabretoothed predators. Zoological Journal of the Linnean Society. 2005;145:393–426.
  82. Kano T. The distribution and habit of mammals of Formosa. Zoological Magazine. 1930;42:165–173.
  83. Hazarika AA. Goat predation by clouded leopard (Neofelis nebulosa) in Kakoi Reserve Forest of Assam. Biodiversity Heritage Library. 1996;93:584–585.
  84. Belbachir F, Pettorelli N, Wacher T, et al. Monitoring rarity: the critically endangered Saharan cheetah as a flagship species for a threatened ecosystem. PLoS One. 2015;10:e0115136.
  85. Allen ML, Elbroch LM, Casady DS, et al. The feeding and spatial ecology of mountain lions (Puma concolor) in Mendocino National Forest, California. PLoS One. 2015;101:51–65.
  86. Bothma JDP, Le Riche EAN. Evidence of the use of rubbing, scent–marking and scratching–posts by Kalahari leopards. Journal of Arid Environments. 1995;29:511–517.
  87. Gibson Hill CA. Notes on the clouded leopard [Neofelis nebulosa (Griffith)]. Biodiversity Heritage Library. 1950;49:543–546.
  88. Mohamad SW, Rayan DM, Christopher WCT, et al. The first description of population density and habitat use of the mainland clouded leopard Neofelis nebulosa within a logged–primary forest in South East Asia. Population Ecology. 2015;57:495–503.
  89. Moo SSB, Froese GZ, Gray TN. First structured camera–trap surveys in Karen State, Myanmar, reveal high diversity of globally threatened mammals. Oryx. 2017;51:1–7.
  90. O Brien SJ, Janice SM, Craig P, et al. Biochemical genetic variation in geographic isolates of African and Asiatic lions. National Geographic Research. 1987;3:114–124.
  91. O Brien SJ, Johnson WE. Big cat genomics. Annual Review. 2005;6:407–429.
  92. Tempa T, Hebblewhite M, Mills LS, et al. Royal Manas National Park, Bhutan: a hot spot for wild felids. Oryx. 2013;47(2):207–210.
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