Northern Tiger Cat
Leopardus tigrinus
A. Sliwa
Description
The tiger cats (Leopardus tigrinus/Leopardus guttulus) are part of the ocelot lineage, one of the youngest of all cat lineages. Their taxonomy poses genetic complications that are only now being understood. They were recently acknowledged as two distinct species, given their genetic differentiation. However, it is likely that the current Central American subspecies, called Leopardus tigrinus oncilla, may also be a different species too. The Costa Rican population and the one of Central and Southern Brazil (now called Leopardus guttulus) have been isolated for approximately 3.7 million years. These two populations show a high level of divergence both populations have a low genetic diversity. To add more genetic complexity, there has been ancient historic hybridisation between the pampas cat (L. colocola) and L. tigrinus, intense hybridisation with margays (L. wiedii) and ocelots (L. pardalis) in Venezuela, Colombia, Ecuador, Bolivia and Argentina, and ongoing bi-directional hybridisation between L. guttulus with the Geoffroy’s cat (L. geoffroyi). However, there has been no indication of mixing whatsoever between the two former single species. In other words, tiger cat populations mix with other species but not with themselves!
Currently two subspecies of the Northern tiger cat are recognised:
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Leopardus tigrinus tigrinus in northern South America, possibly as south as Bolivia and northern Argentina and
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Leopardus tigrinus oncilla in Costa Rica and possibly Panama.
However, further research is needed to establish whether northwestern South American tiger cats are another species L. pardinoides and if the tiger cats from Central America represent a distinct species too.
The tiger cats are small cats with a slender body, proportioned like a slender house cat with body weight ranging from 1.8 kg to 3.5 kg. Both species present similar measurements. Males are consistently slightly larger than females. At first glance, the tiger cat species seem to be cryptic. They do show some subtle differentiation in base colour, spot pattern, and morphology, which are not easy to tell apart and shows slight regional variation within the northern species, too. Northern tiger cats from the western part of their range have a darker base colour varying from dark orange-brown to a brown tinged with yellow or grey. Their rosettes are medium-sized and tend to form small- to medium-sized oblique bands arranged in scapular inguinal direction. Meanwhile, the northern tiger cats from eastern South America have a lighter base colour with a spectrum from light yellow- brown to pale yellow and grey- yellow. Their rosettes are smaller, with usually narrow and discontinuous rims and do not coalesce into oblique bands. The base colour of southern tiger cats (L. guttulus) ranges from dark yellow- brown to ochraceous buff. Their rosettes have thicker, continuous rims, rarely coalescing into smaller oblique bands. The northern tiger cat has a lighter built, with a slender body, legs and tail. The southern tiger cat, on the other hand, tends to look slightly bulkier, with a thicker tail and smaller rounder ears. Nevertheless, individuals of both species can diverge from these norms. The paler belly fur is covered with dark spots. The large ears of both species have a black backside with a central white spot. The southern tiger cat’s tail has seven to thirteen irregular, thin rings and a black tip. The northern tiger cat has a less conspicuously, thinly ringed tail. In both species, the tail measures about 60% of the head and body length. Both tiger cats look very similar to the margay (L. wiedii), making it difficult to distinguish the three. However, the tiger cats’ fur is not as thick, its patterns tend to be less dark and blotchy, with abundant solid dot-like spots and open rosettes, which tend to be smaller and more numerous. The species is slenderer, its paws are proportional to its size and its tail is shorter than the margay’s tail. In all tiger cats the hair on the nape slants backwards, unlike the ocelot and margay, but similar to Geoffroy’s cat.
Melanism is common in both species. In Costa Rica, melanism was found to be more common in dense forests than in more open habitats.
Weight
1.8 - 3.5 kg
Body Length
38 - 59 cm
Tail Length
20 - 42 cm
Longevity
15 -21 years
Litter Size
1 - 4 kittens (avg: 1)
P. Meier
Status and Distribution
The northern tiger cat is classified as Vulnerable in the IUCN Red List and nationally in Colombia and Ecuador. In the whole of Brazil, the species is listed as Endangered, and in the state of Bahia, Brazil, as Vulnerable. Brazil is the main range country for both the northern and southern tiger cat.
Throughout its range the northern tiger cat is considered as widespread but rare. Recently, the first density estimates from camera trapping were established in the Brazilian Cerrado. In the state of Minas Gerais, densities of 4.5 individuals per 100 km² at the Porto Cajueiro Private Reserve and 9.1 individuals per 100 km² at the Grande Sertão Veredas National Park. For two sites in Mirador State Park in the state of Maranhõ, Spatially Explicite Capture Recapture estimates were 8.68 ± 3.9 (3.75–20.1) individuals per 100 km² and 11.3 ± 5 (5.0–25.5) individuals per 100 km², respectively. This results in an estimated population size of 287 (127–661) individuals in Mirador State Park, and with extrapolation to a possible population some 700 individuals in the protected areas of the northern savannas, and of 2,000–3,000 individuals in the states of Maranhão, Tocantins, Piauí and Bahia. In all the study sites previously mentioned, ocelots were present, but rare.
Before those density estimate from camera trapping, densities were largely estimated based on few home range estimates. Population densities in the Cerrado and Caatinga in Brazil were estimated at 1–5/100 km². The northern tiger cat is negatively affected by the ocelot and occurs mainly outside of protected areas. Where the ocelot is not present it is thought to reach densities of 5–20 individuals per 100 km². In some areas declines of 10–40% were estimated. The global population was estimated at 8,932 to 10,208 adult individuals.
The distribution range of the northern tiger cat extends from Costa Rica and Panama in Central America into South America down to Central Brazil. Its southern limits and the extent of a possible overlap with the populations of the southern tiger cat are not yet well known. Its distribution in the Amazon basin is possibly patchy and not continuous. The northern tiger cat is absent from the Darien Peninsula connecting Central and South America, as well as from the Llanos of Venezuela, and the Paraguayan Chaco. In Colombia, it is found along the three Andean mountain chains, but there are no confirmed records in the northern portion of its distribution in Colombia. From Ecuador and Peru, only a few museum specimens exist and only in 2000 was the species formally confirmed in Bolivia through live trapping.
Habitat
The northern tiger cat lives in a wide range of habitats. These include tropical and subtropical rainforest, deciduous/semi-deciduous, montane and premontane forests, semiarid thorny scrub, savannah and wet/swampy savannah. In Central and northwestern South America, the northern tiger cat is mainly associated with montane cloud forests, where it is usually found at higher elevations than the ocelot and margay. The northern tiger cat occurs up to an elevation of 3,000 m, occasionally higher. In Colombia, it seems to be restricted to elevations above 1,500 m but has been recorded up to 4,800 m. Most records in Costa Rica come from the forests along the flanks of volcanos at elevations from 1,000 m up to the tree line where it inhabits cloud and elfin forests. On the other hand, in Brazil it mainly occurs in the lowlands below 500 m and is commonly associated with savannah, semiarid scrub, as well as forests. Even though it is found in Amazonian rainforests, to what degree the northern tiger cat uses this habitat is not clear and needs further investigation. It can be found in disturbed habitats, even close to human settlements, provided there is natural cover and prey. In Antioquia, Colombia, tiger cats were also recorded within cypress and pine plantations. In the Caatinga drylands of Rio Grande do Norte, Brazil, northern tiger cats were more likely to be found away from rural settlements and in areas with a higher proportion of woody vegetation. In Manu National Park, Peru, northern tiger cat occurrence decreased with increasing distance to the park.
P. Meier
Ecology and Behaviour
The tiger cat is a solitary felid. It is active predominantly at night but can also show varying degrees of crepuscular and diurnal activity. In Costa Rica, melanistic northern tiger cats were found to be more diurnal than non-melanistic ones. Melanistic individuals benefit from better camouflage in dense forest under brighter daylight conditions than non-melanistic ones. Generally, diurnal activity is thought to be a strategy to avoid predation by the larger sympatric ocelot. In areas where ocelots occur, both northern and southern tiger cats, as well as the margay and jaguarundi, tend to be rare because of potential intra-guild predation/competition. This negative impact of the ocelot on smaller cat species is called the “ocelot effect”. Thus, tiger cat numbers are negatively impacted by the larger ocelot through interspecific killing to reduce competition. Tiger cat numbers are not affected by the margay and jaguarundi, which are, in fact, more direct competitors for resources than the much larger ocelot.
Northern tiger cat population densities vary but are thought to be lower than expected throughout most of its range. Given its size, expected the density would be 91 individuals per 100 km². However, generally the northern tiger cat occurs at densities of 1–5/100 km², and only in very few and highly localized areas, where ocelots are absent or rare, do they reach densities of up to 15–25/100 km². In the Amazon, usually the safeguard region for the tropical American felids, the northern tiger cat occurs at an exceedingly low density of perhaps only 0.01 individuals per 100 km². There is evidence that it is also naturally rare and elusive in Central America, as it is in some areas of Brazil. It is mostly found outside protected areas perhaps due to the “ocelot effect” and does not seem to attain effective population size for long-term persistence in any Conservation Unit.
Tiger cats are excellent climbers but spend most of their time on the ground as most of its prey is terrestrial. Small prey is killed with a bite to the neck, but larger prey tends to be attacked first from the back. Feeding starts around the head or neck. It seems that both species of tiger cats present very similar habits, which makes it still hard to set them apart ecologically.
Home ranges of the tiger cats are 2.5 times larger than they would be expected, based on the cat’s body size. This may be another consequence of avoiding larger and potential felid predators. Very few studies on home ranges have been conducted. Home ranges for the northern tiger cat ranges from 1 to 17.1 km². Female ranges are smaller than those of males.
The following information about reproduction found in the literature stems from captive individuals and was published before the splitting of L. tigrinus and L. guttulus. Thus, it cannot be attributed with certainty to one or the other species and is presented identically for both: Very little information about the tiger cat’s reproduction is available. Reproduction occurs year-round but could show different peaks in different areas. Oestrus lasts on average for 2.5 (1–6) days, and the mean interoestrous interval is 14.2 (10–26) days. The gestation period lasts for 71–78 days, after which 1–4 cubs are born, (average 1.12). The eyes are open at 8–17 days. Weaning occurs at two to three months and young attain adult body size at 11 months of age. However, sexual maturity is achieved only at about 2–2.5 years, which is rather very late for a felid of this size. The lifetime number of young potentially produced by a seven-year-old female tiger cat in the wild is generally up to five. This shows a very low reproductive potential, considering its small size and in comparison, to other felids from other continents.
Prey
The northern tiger cat's diet is still very poorly studied but is known to be based on small mammals (< 100 g), birds and reptiles (especially lizards). Stomach contents from specimens from Costa Rica and Venezuela included mostly small rodents. Conversely, in the semi-arid Caatinga scrub of northeastern Brazil, the diet comprised 28 items. In this area, mean prey mass was around 55 g. It mainly consisted of lizards, but also included significant proportions of birds and small rodents. This suggests that this small felid is a generalist predator, taking advantage of the most readily available resources in the area. Nevertheless, in the Boqueirão da Onça region, northern Bahia, Brazil, northern tiger cat occupancy was positively correlated with rock cavy (Kerodon rupestris) occupancy. It was speculated that the cavy’s preferential use of rocky outcrops made encounters more predictable and enabled the tiger cats to maximise foraging efficiency.
P. Meier
Main Threats
The main threats to the northern tiger cat are habitat loss and fragmentation due to deforestation and persecution by humans. The cloud forests in Colombia, for example, are being replaced by coffee or eucalyptus plantations, and the Brazilian Cerrado is being converted to cereal crops. Loss of natural cover in the Brazilian Cerrado and Caatinga reaches 55% and 30–50%, respectively. This would thus imply an equivalent reduction in the species’ extent of occurrence. As the tiger cat shows low densities in protected areas and populations are fragmented, it is particularly vulnerable to habitat conversion. Further threats include retaliatory killing due to poultry depredation, and road mortality.
Free-ranging domestic dogs can occur even in protected areas and pose additional threats to the northern tiger cats. Not only are they predators and competitors of the northern tiger cat, but they are also disease vectors e.g. for Parvovirus and Canine Distemper Virus. However, the impact of the diseases on northern tiger cat populations is yet unknown.
Historical trade in tiger cats (which would include both species) from 1976 to 1985 consisted of an astonishing 352,508 skins, which would represent about 28% of all trade in Neotropical felids during this period, second only to Geoffroy’s cat. Although the international trade in furs has been heavily reduced, illegal hunting and capturing still takes place, mostly for the local market. Local communities have a variety of uses for the northern tiger cat: In Peru, trade has been identified both for furs and for pets. In Ecuador it is also used as a pet, as well as food. In the Caatinga, northeastern Brazil, northern tiger cats are used as bushmeat, for medicine, for magical/religious ceremonies, as pets and for ornamental purposes.
Models predict 86.2% range reduction as a result of climate change by 2050 for the northern tiger cat.
Another problem is the lack of knowledge of this cat species. Very little information is available about the northern tiger cat’s ecology and status making it difficult to assess threats and their impact.
Conservation Efforts and Protection Status
The tiger cat is included in the Appendix I of CITES since 1989 and is protected over part of its range. Hunting is prohibited in Brazil, Colombia, Costa Rica, French Guiana, Suriname and Venezuela, but it is not legally protected in Ecuador, Guyana, Nicaragua, Panama and Peru.
As the northern tiger cat, when present, occurs in extremely low numbers in the Amazon Basin reserves or other protected areas, such areas do not represent a sufficient safeguard for this species as they do for other felids. Also, this felid is probably most frequent outside protected areas, where its habitat is undergoing high rates of destruction. Thus, conservation efforts should be focused on the areas outside protected areas. The area with the highest potential for maintaining the largest population of the northern tiger cat is the conservation complex around Nascentes do Rio Parnaíba National Park (Brazil) in the northern savannas. However, this is based on estimates and predictive modelling and numbers are expected to vary from 750 to 2,250 individuals.
Further research on both species of the tiger cat’s ecology, natural history and threats is urgently needed. Reassessment of its taxonomy is a research priority as the northern tiger cat may possibly be divided into two separate species.
