|An adult male Himalayan tahr in Kedarnath Wildlife Sanctuary, Uttarakhand|
The Himalayan tahr (Hemitragus jemlahicus) is a large even-toed ungulate native to the Himalayas in southern Tibet, northern India, western Bhutan and Nepal. It is listed as Near Threatened on the IUCN Red List, as the population is declining due to hunting and habitat loss. 
A recent phylogenetic analysis indicates that the genus Hemitragus is monospecific, and that the Himalayan tahr is a wild goat. 
The Himalayan tahr has been introduced to Argentina, New Zealand, South Africa and the United States.  
Tahr belong to the subfamily Caprinae in the order Artiodactyla. Their closest relatives in the subfamily Caprinae are sheep and goats.  A subspecies, the Eastern Himalayan tahr or shapi, was described in 1944.  This classification is not considered valid anymore, and no subspecies are currently recognized. 
The word "tahr," first used in English writings in 1835, is derived from the animal's local name in the Western Himalayas, which has otherwise been rendered as "tehr," "tare" and "tahir". Through confusion with thār, a Nepali word for the Himalayan serow, it has also been spelled "thar." 
The genus name Hemitragus is derived from the Greek words hēmi- meaning "half" and trágos meaning "goat".  
The Himalayan tahr has a small head, small pointed ears, large eyes, and horns that vary between males and females.  Their horns reach a maximum length of 46 centimetres (18 in). Himalayan tahrs are sexually dimorphic, with females being smaller in weight and in size and having smaller horns. The horn is curved backwards, preventing injury during mating season when headbutting is a common mating ritual among males. The average male tahr usually weighs around 73 kg (161 lb), with females averaging 36 kg (79 lb) and is shorter in height than in length.  The exterior of a tahr is well adapted to the harsh climate of the Himalayans. They sport thick, reddish wool coats and thick undercoats, indicative of the conditions of their habitat. Their coats thin with the end of winter and becomes lighter in color.  This shedding is presumably an adaptation that allows their internal body temperatures to adjust to the harsh temperatures of the Himalayan Mountains.[ citation needed ]
As a member of the ungulate group of mammals, the Himalayan tahr possesses an even number of toes. They have adapted the unique ability to grasp both smooth and rough surfaces that are typical of the mountainous terrain on which they reside. This useful characteristic also helps their mobility. The hooves of the tahr have a rubber-like core which allows for gripping smooth rocks while keratin at the rim of their hooves allow increased hoof durability, which is important for traversing the rocky ground. This adaptation allows for confident and swift maneuvering of the terrain. 
The lifespan of a Himalayan tahr typically ranges around 14 or 15 years, with females living longer than males. The oldest known Himalayan tahr lived to 22 years old in captivity. 
The Himalayan tahr is adapted to life in a cool climate with rocky terrain, which allows them to be found in mountainous areas. In the Himalayas, they are mainly found on slopes ranging from 2,500 to 5,000 m. Himalayan tahr can eat a wide variety of plants. They most often inhabit locations where vegetation is exposed for browsing and grazing. During the winter (when snow covers vegetation at higher elevations), they are found on lower-altitude slopes. 
The herbivorous diets of the Himalayan tahrs leave them spending most of their time grazing on grasses and browsing on leaves and some fruits.  Their short legs allow them to balance while reaching for the leaves of shrubs and small trees.  The tahr consumes more woody plants than herb species  with as much as 75% of the tahr diet consisting of natural grasses.  The tahr, like most members of the bovid family, are ruminants and have complex digestive systems . A multi-chambered stomach allows the tahr to repeatedly regurgitate its food, chew it, and obtain nutrients from otherwise indigestible plant tissues.
Tahr are preyed upon by snow leopards. 
Tahrs are polygynous, and males are subject to stiff competition for access to females. Young reproductive males roam and mate opportunistically (when larger males are not present), while more mature males (more than four years old) will engage in ritualistic behavior and fighting to secure mates. During mating season, reproductive males lose much of their fat reserves, while females and nonreproductive males do not, indicating a substantial cost to these behaviors.  Factors that contribute to which males dominate include size, weight, and testosterone levels. Coat color can have an effect; Himalayan tahrs with lighter coats are more likely to gain access to estrous females  Himalayan tahrs have precocious young which can stand soon after birth.  Females have a gestation period of 180–242 days, usually with a litter size of only one kid.   This indicates sexual selection can be extremely important to the fitness of males.
During the rut, male Himalayan tahrs often compete with other males for access to females. Factors that contribute to reproductive success include large body size, large horn size, and high aggression. Coat color is a factor that determines rank among Himalayan tahrs, and males with light coats mate more often.  In addition, the horns of the male are often used in the ritual process to court female tahrs (either for display purposes or, less often, for direct combat), although these horns can also serve as a defense mechanisms against potential predators. 
Other ungulate herbivores with overlapping natural ranges include bharal, argali, and goral. Removal experiments (in which one of the hypothesized competitors is removed, and the effect on the other species is observed) have not been conducted to determine empirically that competition is actually occurring, but the animals do share food resources.  Competition can occur when two or more species share a limited resource, such as particular food sources, in a given area. Since the Himalayan tahr and the other ungulates are eating the same foods, competition possibly is occurring among them.
This section needs additional citations for verification .(July 2020)
A key factor contributing to the success of the Himalayan tahr as an invasive species is their mobility. During the night, they move to locations with lower elevations to have better access to resources such as food and water, whereas during the day, they move to locations with higher elevation to rest and avoid predators.  This mobile behavior not only allows them to seek refuge from predators, but also allows them to have access to resources over a large area.
Another key characteristic that allows Himalayan tahr to be successful as an invasive species is their digestive tract. Their digestive system allows them to consume a wide variety of vegetation ranging from easy-to-digest leaves/grasses to woody shrubs and other “tough” vegetation not as easily digested by other species. This flexibility in diet not only allows Himalayan tahr to have a competitive advantage for resource use in their environment among other species, but it also allows them to be less hindered by abiotic disruptions and other natural disasters. In other words, their ability to digest a large range of vegetation allows the Himalayan tahr to have a bigger fundamental niche, and as a result, increases their success as an invasive species. 
Lastly, the Himalayan tahr lacks predators in the regions where it has been introduced, so is only limited by access to food and water, and its own reproductive rate. 
The tahr was introduced into Argentina in 2006 by private individuals, presumably for hunting purposes. The importation has been deemed successful, but it is too soon to determine whether it will be detrimental to the environment.  The IUCN lists the tahr as being possibly extirpated from Argentina despite its introduction.
Himalayan tahr were introduced to New Zealand in 1904 around the Mount Cook region for sport and have since expanded rapidly into neighboring areas. Their heavy grazing of native plants in New Zealand has caused significant environmental damage.   They currently inhabit a portion of the Southern Alps / Kā Tiritiri o te Moana and are still being hunted for sport.   The Department of Conservation (DOC) culled 12,000 tahr between July 2019 and February 2020, and over 7,000 between July and November 2020.  
Groups such as hunters and farmers have resisted tahr eradication. A report prepared in 2005 by Kenneth F.D. Hughey and Karen M. Wason presented the results of a survey conducted among 43 farmers living within tahr distribution.  Roughly 80% of farmers view tahr as a resource, not as a threat. The respondents indicated they placed conservational and commercial value (live animal/meat, hunting, farming) on tahr. Thirty six percent of these farmers also reported to having earned at least $1,000 a year in profit from having tahr on their property, with the highest earnings being above $50,000 (Table 5.5 of that study), usually as a result of allowing professionally guided hunters on their property.  Also, a 1988 study showed that hunters spent $851 per person per year on hunting, with expenses being greatest for big-game targets, such as the Himalayan tahr. 
Tahr could be eradicated from New Zealand but "this has not happened due to intense lobbying pressure from hunting interests, so ongoing ecological costs are incurred by the natural environment." 
The hunting lobby has protested against the culling of tahr in 2020.    DOC released a management plan for 2020–2021 which was contested in the High Court. The Court ruled that DOC should consult with interested parties and stakeholders which resulted in a number of changes to the plan; the revised plan was welcomed by the Tahr Foundation.   
A negative impact the Himalayan tahrs have on their environment is increased herbivory on the native vegetation of the ecosystem, which can make it harder for other herbivores to find food. The increased herbivory can also lead to a decrease in soil nutrients, such as oxygen, nitrates, and ammonia, resulting in positive feedback loop, making it harder for plants to grow at all. Consequently, the natural fauna of the ecosystem is heavily affected. This increase has also resulted in poor soil quality in many environments occupied by the Himalayan tahr and has severely limited the presence of certain plant species.   The lack of certain vegetation, in turn, may affect animal species that rely on them as a food source. 
Data on the rapid expansion of the tahr are documented by government agencies. Over a time span of 16 years, the Himalayan tahr reached up to 33 tahr/km2 in New Zealand – twice the initial population (2*N0). Without regulated hunting or the presence of natural barriers, the Himalayan tahr can pose a large threat to the indigenous fauna and flora populations within the area. 
In 1930, the Himalayan tahr was denied protection by the Animals Protection and Game Act (1921–22) and was recognized as a danger to the environment,  although the species is still considered to be endangered in the Himalayas on the IUCN Red List.  Since 1937, various government operations have been undertaken to reduce tahr population and/or keep it at fixed numbers. The control of tahr remains ecologically and economically significant because of their widespread destruction of native flora and fauna and their valuable capture for hunters, respectively.
In 1993, the Department of Conservation prepared the Himalayan Tahr Control Plan which lists “aerial game recovery operations, recreational and safari hunting as primary means of control”.  Under the plan, the area of the tahr distribution was divided into two exclusion zones and seven management units. The exclusion zones set boundaries on the area that the tahr inhabits, with the official control operations to be employed to prevent them from spreading beyond those zones. The management unit has a fixed maximum density, which varies from 1–2.5 tahr/km2 and is considered to be low enough to have a minimal negative impact on the ecosystem and, even, restore native vegetation. Under these conditions, the plan aimed to keep tahr numbers below 10,000 throughout the South Island.  Since then, the Department of Conservation has been actively advertising tahr hunting and has created 59 tahr-hunting areas. Hunting remains the primary means of control.
In 1960, sodium monofluoroacetate (also known as compound 1080) was used to poison tahrs.  This derivative of fluoroacetic acid is commonly used in many countries such as Mexico, Australia, the United States, and New Zealand as a pesticide. Compound 1080 is highly water-soluble and is diluted by rainwater and broken down by aquatic microorganisms.  Water samples after baiting operations did not reveal dangerous levels of the compound.  In the soil, sodium monofluoroacetate is converted by bacteria and fungi to metabolic products, shown to be nonhazardous to the environment. 
According to Australia's Department of Primary Industries, Parks, Water, and Environment,  mammals (particularly cats and dogs) are the most susceptible to compound 1080 poisoning. Fish, birds, and amphibians generally are highly tolerant to the poison.  Although compound 1080 is a strong enough pesticide to eradicate the entire tahr population, political pressures from hunter groups hinder its use. Opposition by the general public also contributes to the decreased use of 1080 with concerns that the accumulation of 1080 at higher levels of the food chain will pose danger to mammals such as dogs, deer and pigs. 
The Himalayan tahr was introduced to South Africa when in the 1930s, two Himalayan tahrs escaped from a zoo in Cape Town. Subsequent populations of tahrs have descended from the original escaped pair and spread quickly over the Cape Peninsular mountain range.  Most of the population has been culled to make way for the reintroduction of the indigenous antelope, the klipspringer.
The Himalayan tahr is present in New Mexico, where it has been introduced. According to the New Mexico Department of Game and Fish news release dated 28 May 2014, "Only one Wildlife Management Area, Water Canyon, allows hunting for nongame species as a management tool for the non-native Himalayan tahr, a large ungulate related to the wild goat." However, outside of Water Canyon Wildlife Management Area, Himalayan tahr may be taken. There is no closed season or bag limit on Himalayan tahr, and they may be hunted even with an airgun.
Tahrs or tehrs are large artiodactyl ungulates related to goats and sheep. There are three species, all native to Asia. Previously thought to be closely related to each other and placed in a single genus, Hemitragus, genetic studies have since proven that they are not so closely related and they are now considered as members of three separate monotypic genera: Hemitragus is now reserved for the Himalayan tahr, Nilgiritragus for the Nilgiri tahr, and Arabitragus for the Arabian tahr.
The goa, also known as the Tibetan gazelle, is a species of antelope that inhabits the Tibetan plateau.
The subfamily Caprinae, also sometimes referred to as the tribe Caprini, is part of the ruminant family Bovidae, and consists of mostly medium-sized bovids. A member of this subfamily is called a caprine, or, more informally, a goat-antelope.
The chamois or Alpine chamois is a species of goat-antelope native to mountains in Europe, from west to east, including the Alps, the Dinarides, the Tatra and the Carpathian Mountains, the Balkan Mountains, the Rila–Rhodope massif, Pindus, the northeastern mountains of Turkey, and the Caucasus. The chamois has also been introduced to the South Island of New Zealand. Some subspecies of chamois are strictly protected in the EU under the European Habitats Directive.
The Nilgiri tahr is an ungulate that is endemic to the Nilgiri Hills and the southern portion of the Western and Eastern Ghats in the states of Tamil Nadu and Kerala in southern India. It is the state animal of Tamil Nadu. Despite its local name, it is more closely related to the sheep of the genus Ovis than the ibex and wild goats of the genus Capra. It is the only species in the genus Nilgiritragus.
Lake Pukaki is the largest of three roughly parallel alpine lakes running north–south along the northern edge of the Mackenzie Basin on New Zealand's South Island. The others are Lakes Tekapo and Ohau. All three lakes were formed when the terminal moraines of receding glaciers blocked their respective valleys, forming moraine-dammed lakes. The Alps2Ocean mountain bike trail follows the edge of Lake Pukaki for part of its length.
The Nile lechwe or Mrs Gray's lechwe is an endangered species of antelope found in swamps and grasslands in Sudan and Ethiopia.
The markhor is a large Capra species native to Central Asia, the Karakoram, and the Himalayas. It is listed on the IUCN Red List as Near Threatened since 2015.
The blackbuck, also known as the Indian antelope, is an antelope native to India and Nepal. It inhabits grassy plains and lightly forested areas with perennial water sources. It stands up to 74 to 84 cm high at the shoulder. Males weigh 20–57 kg (44–126 lb), with an average of 38 kg (84 lb). Females are lighter, weighing 20–33 kg (44–73 lb) or 27 kg (60 lb) on average. Males have 35–75 cm (14–30 in) long, ringed horns, though females may develop horns as well. The white fur on the chin and around the eyes is in sharp contrast with the black stripes on the face. The coats of males show a two-tone colouration; while the upper parts and outsides of the legs are dark brown to black, the underparts and the insides of the legs are white. Females and juveniles are yellowish fawn to tan. The blackbuck is the sole living member of the genus Antilope and was scientifically described by Carl Linnaeus in 1758. Two subspecies are recognized.
In biology, culling is the process of segregating organisms from a group according to desired or undesired characteristics. In animal breeding, it is the process of removing or segregating animals from a breeding stock based on specific trait. This is done to exaggerate desirable characteristics, or to remove undesirable characteristics by altering the genetic diversity of the population. For livestock and wildlife, culling often refers to the act of killing removed animals based on their individual characteristics, such as their sex or species membership, or as a means of preventing infectious disease transmission.
Gangotri National Park is a national park in Uttarkashi District of Uttarakhand in India, covering about 2,390 km2 (920 sq mi). Its habitat consists of coniferous forests, alpine meadows and glaciers. Gaumukh at Gangotri glacier, the origin of river Ganga, is located inside the park. Gangotri National Park was established in 1989.
The white-bellied musk deer or Himalayan musk deer is a musk deer species occurring in the Himalayas of Nepal, Bhutan, India, Pakistan and China. It is listed as endangered on the IUCN Red List because of overexploitation resulting in a probable serious population decline.
The Arabian tahr is a species of tahr native to eastern Arabia. Until recently, it was placed in the genus Hemitragus, but genetic evidence supports its removal to a separate monotypic genus, Arabitragus.
The Australian painted lady is a species of butterfly mostly confined to Australia, although westerly winds have dispersed it to islands east of Australia, including New Zealand. Debate surrounds the taxonomy of this species. Some believe that the Australian painted lady should be a subspecies of the painted lady due to the similarity in lifestyle and behaviour. Furthermore, the painted lady is found around the globe, but Australia is the only location in which it varies enough to be considered a separate species.
The Western Himalayan alpine shrub and meadows is a montane grasslands and shrublands ecoregion of Nepal, India, and Tibet, which lies between the tree line and snow line in the western portion of the Himalaya Range.
The feral goat is the domestic goat when it has become established in the wild. Feral goats occur in many parts of the world.
Graeme James Caughley was a New Zealand population ecologist, conservation biologist, and researcher. He combined empirical research with mathematical models, and supported the declining population paradigm.
Hunting is a popular recreational pursuit and a tourist activity in New Zealand with numerous books and magazines published on the topic. Unlike most other developed countries with a hunting tradition, there are no bag-limits or seasons for hunting large game in New Zealand. Hunting in national parks is a permitted activity. The wide variety of game animals and the limited restrictions means hunting is a popular pastime which has resulted in a high level of firearms ownership among civilians.
In biology, overabundant species refers to an excessive number of individuals and occurs when the normal population density has been exceeded. Increase in animal populations is influenced by a variety of factors, some of which include habitat destruction or augmentation by human activity, the introduction of invasive species and the reintroduction of threatened species to protected reserves.