Indochinese leopard | |
---|---|
An Indochinese leopard at Saigon Zoo and Botanical Gardens | |
Scientific classification | |
Domain: | Eukaryota |
Kingdom: | Animalia |
Phylum: | Chordata |
Class: | Mammalia |
Order: | Carnivora |
Suborder: | Feliformia |
Family: | Felidae |
Subfamily: | Pantherinae |
Genus: | Panthera |
Species: | |
Subspecies: | P. p. delacouri |
Trinomial name | |
Panthera pardus delacouri Pocock, 1930 |
The Indochinese leopard (Panthera pardus delacouri) is a leopard subspecies native to mainland Southeast Asia and southern China. In Indochina, leopards are rare outside protected areas and threatened by habitat loss due to deforestation as well as poaching for the illegal wildlife trade. In 2016, the population was previously thought to comprise 973–2,503 mature individuals, with only 409–1,051 breeding adults. The historical range had decreased by more than 90%. [2] However, as of 2019, it is estimated that there are 77-766 mature Indochinese leopards and that their numbers are decreasing. [1]
Panthera pardus delacouri was described in 1930 by Reginald Innes Pocock based on a leopard skin from Annam. [3]
Pocock described an Indochinese leopard skin as almost rusty-red in ground colour but paler at the sides. It had small rosettes that were mostly 3.8 cm × 3.8 cm (1.5 in × 1.5 in) in diameter and so closely set that it looked dark. The fur was short with less than 2.5 cm (0.98 in) long hair on the back. He commented to have seen only black leopards from Johor and other areas in the Malay Peninsula exhibited in menageries. He therefore assumed that the proportion of black leopards increases farther south. [3]
Records from camera trapping studies conducted at 22 locations in southern Thailand and peninsular Malaysia between 1996 and 2009 show that Indochinese leopards recorded north of the Kra Isthmus are predominantly spotted. South of the Isthmus, only melanistic leopards were recorded. [4] Melanism is quite common in dense tropical forest habitat, and black leopards are thought to have a selective advantage for ambush. [5]
The Indochinese leopard is distributed in Southeast Asia, where today small populations remain only in Myanmar, Thailand, Peninsular Malaysia, Cambodia and southern China. [1]
In Myanmar's Chatthin Wildlife Sanctuary, the leopard population declined so drastically between the 1940s and 1980s, that by 2000 it was estimated as being close to locally extinct. [6] In 2015, leopards were recorded for the first time by camera traps in the hill forests of Karen State. [7] The Northern Tenasserim Forest Complex on the Thailand-Myanmar border was considered a stronghold in 2016. [2]
In Thailand, the Indochinese leopard is present in the Western Forest Complex, Kaeng Krachan-Kui Buri and Khlong Saeng-Khao Sok protected area complexes. But since the turn of the 21st century, it has not been recorded any more in the northern and south-central forest complexes of the country. [2] In Hala Bala Wildlife Sanctuary on the Thai-Malaysian border, only two leopards walked past camera traps deployed between October 2004 and October 2007. [8]
In Malaysia, the leopard is present in Belum-Temengor, Taman Negara and Endau-Rompin National Parks. [2] In April 2010, a spotted leopard was seen in a camera trap in Taman Negara National Park, where previously only black leopards were thought to occur. [4] It has also been recorded in secondary forests in Selangor and Johor states. [9] [10]
In Laos, 25 different leopards walked past camera traps set up over an area of 500 km2 (190 sq mi) in the Nam Et-Phou Louey National Biodiversity Conservation Area between April 2003 and June 2004. [11] In 2010, leopards were reported to also occur in Nam Kan National Protected Area. [12] Due to absence of records, leopards are suspected to have been extirpated in the country as of 2019. [1]
In Cambodia, leopards were recorded in deciduous dipterocarp forest in Phnom Prich Wildlife Sanctuary between December 2008 and August 2009, and in Sre Pok Wildlife Sanctuary in 2009 and 2014. [13] [14] [15] In 2021, no individual was detected in eastern Cambodia, indicating that this population was also extirpated. [16]
In southern China, camera trap surveys were conducted in 11 nature reserves between 2002 and 2009, but leopards were only recorded in Changqing National Nature Reserve in the Qinling Mountains. [17]
Since the mid-1980s, leopard-oriented field research was carried out in three protected areas in Thailand:
Wild boar, macaque and lesser mouse deer were identified as the main potential prey species for the leopard in a highly fragmented secondary forest in Malaysia's Selangor area. [22]
There are few contiguous areas left where leopards have a chance of long-term survival. They are primarily threatened by habitat destruction following large–scale deforestation, and prey depletion through illegal hunting. [19] [21] [23]
An increasingly growing threat is hunting for the illegal wildlife trade, which is showing its potential to do maximum harm in minimal time: [24] leopards are increasingly being used as substitutes for tiger parts in traditional Chinese medicine, with the price of leopard parts rising as tiger parts become scarce. [2]
Human traffic inside protected areas negatively affects leopard movements and activity. They show less diurnal activity in areas more heavily used by people. [25] In villages located in Laos' protected areas, local people consume about 28.2 kg (62 lb) meat of deer and wild boar annually per household. This offtake amounts to 2,840 kg (6,260 lb) ungulates per 100 km2 (39 sq mi), which is equivalent to the meat required to sustain several leopards per 100 km2 (39 sq mi). [11] [26]
In a highly fragmented tropical rain forest within Malaysia's capital agglomeration of Klang Valley leopard density has been estimated at 28.35 individuals per 100 km2 (39 sq mi), which is one of the highest leopard densities reported. As a result of rapid shrinking of the forests, individuals may have been pushed into the remaining forest in this area, so that their population is unexpectedly high. Leopards were mostly affected by construction activities conducted inside the forest. [9]
Substantial domestic skin markets exist in Myanmar, in Malaysia for traditional medicines, and in China for skins and bones, the latter particularly as a substitute for the tiger in traditional Asian medicines and tonics. In China, the use of stockpiles of leopard bone is still permitted by the government by medicinal manufacturers, despite the domestic trade ban. [27]
In Myanmar, 215 body parts of at least 177 leopards were observed in four markets surveyed between 1991 and 2006. Among the body parts, a leopard penis and testes were openly traded, along with other parts of freshly killed animals. Three of the surveyed markets are situated on international borders with China and Thailand, and attract international buyers, although leopards are completely protected under Myanmar's national legislation. Effective implementation and enforcement of CITES is considered inadequate. [28]
In early 2018, the carcass of a black leopard was discovered in Thailand's Thung Yai Naresuan Wildlife Sanctuary, along with other animals. [29] [30] They were in the possession of a businessman who presided over the construction company Italian-Thai Development. [31]
The tiger is a large cat and a member of the genus Panthera native to Asia. It has a powerful, muscular body with a large head and paws, a long tail and orange fur with black, mostly vertical stripes. It is traditionally classified into nine recent subspecies, though some recognise only two subspecies, mainland Asian tigers and the island tigers of the Sunda Islands.
A black panther is the melanistic colour variant of the leopard and the jaguar. Black panthers of both species have excess black pigments, but their typical rosettes are also present. They have been documented mostly in tropical forests, with black leopards in Africa and Asia, and black jaguars in South America. Melanism is caused by a recessive allele in the leopard, and by a dominant allele in the jaguar.
The leopard is one of the five extant cat species in the genus Panthera. It has a pale yellowish to dark golden fur with dark spots grouped in rosettes. Its body is slender and muscular reaching a length of 92–183 cm (36–72 in) with a 66–102 cm (26–40 in) long tail and a shoulder height of 60–70 cm (24–28 in). Males typically weigh 30.9–72 kg (68–159 lb), and females 20.5–43 kg (45–95 lb).
The clouded leopard, also called mainland clouded leopard, is a wild cat inhabiting dense forests from the foothills of the Himalayas through Northeast India and Bhutan to mainland Southeast Asia into South China. It was first described in 1821 on the basis of a skin of an individual from China. The clouded leopard has large dusky-grey blotches and irregular spots and stripes reminiscent of clouds. Its head-and-body length ranges from 68.6 to 108 cm with a 61 to 91 cm long tail. It uses its tail for balancing when moving in trees and is able to climb down vertical tree trunks head first. It rests in trees during the day and hunts by night on the forest floor.
The Indochinese tiger is a population of the Panthera tigris tigris subspecies that is native to Southeast Asia. This population occurs in Myanmar and Thailand. In 2011, the population was thought to comprise 342 individuals, including 85 in Myanmar and 20 in Vietnam, with the largest population unit surviving in Thailand, estimated at 189 to 252 individuals during the period 2009 to 2014.
The Arabian leopard is the smallest leopard subspecies. It was described in 1830 and is native to the Arabian Peninsula, where it was widely distributed in rugged hilly and montane terrain until the late 1970s. Today, the population is severely fragmented and thought to decline continuously. In 2008, an estimated 45–200 individuals in three isolated subpopulations were restricted to western Saudi Arabia, Oman and Yemen. However, as of 2023, it is estimated that 100–120 in total remain, with 70-84 mature individuals, in Oman and Yemen, and it is possibly extinct in Saudi Arabia. The current population trend is suspected to be decreasing.
The Sri Lankan leopard is a leopard subspecies native to Sri Lanka. It was first described in 1956 by Sri Lankan zoologist Paules Edward Pieris Deraniyagala.
The Indian leopard is a subspecies of the leopard widely distributed on the Indian subcontinent. It is threatened by illegal trade of skins and body parts, and persecution due to human-leopard conflict and retaliation for livestock depredation.
Panthera pardus tulliana, also called Persian leopard,Anatolian leopard, and Caucasian leopard in different parts of its range, is a leopard subspecies that was first described in 1856 based on a zoological specimen found in western Anatolia. It is native to the Iranian Plateau and the surrounding region from eastern Anatolia and the Caucasus to the Hindu Kush, where it inhabits foremost subalpine meadows, temperate broadleaf and mixed forests and rugged ravines at elevations of 600 to 3,800 m. It preys mostly on ungulates reliant on these habitats.
Tiger conservation attempts to prevent tigers from becoming extinct and preserving its natural habitat. This is one of the main objectives of the international animal conservation community. The Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES) has played a crucial role in improving international efforts for tiger conservation.
The Western Forest Complex (WEFCOM) is a large natural conservation area in Thailand, located in the country's western region along its border with Myanmar. It covers 12 national parks and 7 wildlife sanctuaries, and serves as the main biodiversity conservation corridor of the region. Covering 18,730 km2, it is one of the largest protected territories in Southeast Asia. The geography of the Western Forest Complex ranges from lowlands to the mountains of the Thai highlands and the Dawna-Tenasserim Hills.
Hukaung Valley Wildlife Sanctuary is a protected area in northern Myanmar, covering 17,373.57 km2 (6,707.97 sq mi). It was established in 2004 and extended to its present size in 2010. It was initially gazetted in 2004 with an area of 6,371 km2 (2,460 sq mi) in Tanaing Township and extended to Kamaing, Nayun and Kamti Townships. In elevation, it ranges from 125 to 3,435 m in the Hukawng Valley located in Kachin State and Sagaing Region. It harbours evergreen and mixed deciduous forests.
Htamanthi Wildlife Sanctuary is a 2,150.73 km2 (830.40 sq mi) large protected area in northern Myanmar. It was established in 1974 in the Sagaing Region.
The Central Indochina dry forests are a large tropical and subtropical dry broadleaf forests ecoregion in Southeast Asia.
Khao Laem National Park is a park of about 1,500 square kilometers in Western Thailand, located near Myanmar in the northern area of the Tenasserim Hills, Kanchanaburi Province. It is a part of the Western Forest Complex, a system of protected wilderness in the Dawna-Tenasserim Hills area of western Thailand.
The Tenasserim–South Thailand semi-evergreen rain forests is a tropical moist broadleaf forest ecoregion on Mainland Southeast Asia. The ecoregion extends north–south along the Kra Isthmus. It includes lowland forests along the coasts, and montane forests on the Tenasserim Hills and Bilauktaung range, which form the mountainous spine of the isthmus.
Tanintharyi Nature Reserve is a strict nature reserve in Myanmar's Tenasserim Hills, covering 1,699.99 km2 (656.37 sq mi). In elevation, it ranges from at an elevation of 20–130 m (66–427 ft). Most of the tropical rain forest is evergreen, interspersed with some grassland. The reserve provides habitat to Asian elephant and Gurney's pitta. It was gazetted in 2005 for the maintenance of natural resources, scientific research and education of local people in surrounding communities.
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Panlaung and Padalin Cave Wildlife Sanctuary is a protected area in Myanmar's Shan State near Ywangan Township, stretching over an area of 333.8 km2 (128.9 sq mi). It was established in 2002 under the Wildlife Protection Act of 1936. In elevation, it ranges from 150 to 1,555 m covering mixed deciduous and dipterocarp forest.
Kaeng Krachan Forest Complex is the inscribed name of a UNESCO World Heritage Site in Thailand. It covers the areas of Kaeng Krachan, Kui Buri and Chaloem Phrakiat Thai Prachan national parks, and Mae Nam Phachi Wildlife Sanctuary, in the Ratchaburi, Phetchaburi and Prachuap Khiri Khan provinces of Western Thailand, on the country's border with Myanmar. The site was inscribed on the World Heritage list in 2021.