Search This Blog

Wednesday, March 15, 2023

Pleistocene Park

From Wikipedia, the free encyclopedia
Pleistocene Park
Плейстоценовый парк
Ice age fauna of northern Spain - Mauricio Antón.jpg
Depiction of some mammals common in northern Eurasia during the late Pleistocene, by Mauricio Antón. From left to right: wild horse, woolly mammoth, reindeer, cave lion and woolly rhinoceros.
 
Pleistocene Park is located in Russia
Pleistocene Park
LocationRussian Arctic, Sakha Republic
Nearest cityChersky
Coordinates68°30′48″N 161°31′32″ECoordinates: 68°30′48″N 161°31′32″E
Area20 km2 (8 sq mi)
Established1988 / 1996
FounderSergey Zimov
DirectorNikita Zimov
Websitepleistocenepark.de/en/ Edit this at Wikidata

Pleistocene Park (Russian: Плейстоценовый парк, romanizedPleystotsenovyy park) is a nature reserve on the Kolyma River south of Chersky in the Sakha Republic, Russia, in northeastern Siberia, where an attempt is being made to re-create the northern subarctic steppe grassland ecosystem that flourished in the area during the last glacial period.

The project is being led by Russian scientists Sergey Zimov and Nikita Zimov, testing the hypothesis that repopulating with large herbivores (and predators) can restore rich grasslands ecosystems, as expected if overhunting, and not climate change, was primarily responsible for the extinction of wildlife and the disappearance of the grasslands at the end of the Pleistocene epoch.

The aim of the project is to research the climatic effects of the expected changes in the ecosystem. Here the hypothesis is that the change from tundra to grassland will result in a raised ratio of energy emission to energy absorption of the area, leading to less thawing of permafrost and thereby less emission of greenhouse gases. It is also thought that removal of snow by large herbivores will further reduce the permafrost's insulation.

To study this, large herbivores have been released, and their effect on the local fauna is being monitored. Preliminary results point at the ecologically low-grade tundra biome being converted into a productive grassland biome and at the energy emission of the area being raised.

Research goals

Effects of large herbivores on the arctic tundra/grasslands ecosystem

The primary aim of Pleistocene Park is to recreate the mammoth steppe (ancient taiga/tundra grasslands that were widespread in the region during the last ice age). The key concept is that animals, rather than climate, maintained that ecosystem. Reintroducing large herbivores to Siberia would then initiate a positive feedback loop promoting the reestablishment of grassland ecosystems. This argument is the basis for rewilding Pleistocene Park's landscape with megafauna that were previously abundant in the area, as evidenced by the fossil record.

The grassland-steppe ecosystem that dominated Siberia during the Pleistocene disappeared 10,000 years ago and was replaced by a mossy and forested tundra and taiga ecosystem. Concurrently, most of the large herbivores that roamed Siberia during the Pleistocene have vanished from the region. The mainstream explanation for this used to be that at the beginning of the Holocene the arid steppe climate changed into a humid one, and when the steppe vanished so did the steppe's animals. Sergei Zimov points out that in contradiction to this scenario:

  • Similar climatic shifts occurred in previous interglacial periods without causing such massive environmental changes.
  • Those large herbivores of the former steppe that survived until today (e.g. musk oxen, bison, horses) thrive in humid environments just as well as in arid ones.
  • The climate (both temperatures and humidity) in today's northern Siberia is in fact similar to that of the mammoth steppe. The radiation aridity index for northern Siberia on Mikhail Budyko's scale is 2 (= steppe bordering on semi-desert). Budyko's scale compares the ratio of the energy received by the earth's surface to the energy required for the evaporation of the total annual precipitation. The 'humid climate' argument was based on other scales, which compare precipitation to potential evapotranspiration. Moss has a very low transpiration rate and thus causes humidity without necessarily needing humidity for its establishment. Using these other scales as a proof for humidity being the cause of the disappearance of the grasslands therefore constitutes a circular argument, which is not scientifically viable.

Zimov and colleagues argue for a reversed order of environmental change in the mammoth steppe. Humans, with their constantly improving technology, overhunted the large herbivores and led to their extinction and extirpation. Without herbivores grazing and trampling over the land, mosses, shrubs and trees were able to take over and replace the grassland ecosystem. If the grasslands were destroyed because herbivore populations were decimated by human hunting, then "it stands to reason that those landscapes can be reconstituted by the judicious return of appropriate herbivore communities."

Effects of large herbivores on permafrost and global warming

A secondary aim is to research the climatic effects of the expected changes in the ecosystem. Here the key concept is that some of the effects of the large herbivores, such as eradicating trees and shrubs or trampling snow, will result in a stronger cooling of the ground in the winter, leading to less thawing of permafrost during summer and thereby less emission of greenhouse gases.

Permafrost is a large global carbon reservoir that has remained frozen throughout much of the Holocene. Due to recent climate change, the permafrost is beginning to thaw, releasing stored carbon and forming thermokarst lakes. When the thawed permafrost enters the thermokarst lakes, its carbon is converted into carbon dioxide and methane and released into the atmosphere. Methane is a potent greenhouse gas and the methane emissions from thermokarst lakes have the potential to initiate a positive feedback cycle in which increased atmospheric methane concentrations lead to amplified global climate change, which in turn leads to more permafrost thaw and more methane and carbon dioxide emissions.

As the combined carbon stored in the world's permafrost (1670 Gt) equals about twice the amount of the carbon currently released in the atmosphere (720 Gt), the setting in motion of such a positive feedback cycle could potentially lead to a runaway climate change scenario. Even if the ecological situation of the arctic were as it was 400,000 years ago (i.e., grasslands instead of tundra), a global temperature rise of 1.5 °C (2.7 °F) relative to the pre-industrial level would be enough to start the thawing of permafrost in Siberia. An increased cooling of the ground during winter would raise the current tipping point, potentially delaying such a scenario.

Implementation

Background: regional Pleistocene ecoregions

Saigas are extinct in Europe and are a critically endangered species.

It has been proposed that the introduction of a variety of large herbivores will recreate their ancient ecological niches in Siberia and regenerate the Pleistocene terrain with its different ecological habitats such as taiga, tundra, steppe and alpine terrain.

The main objective, however, is to recreate the extensive grasslands that covered the Beringia region in the late Pleistocene. This form of grassland (also known as mammoth steppe) was inhabited by a diverse set of large and medium herbivores. Back in the Pleistocene the area was populated by many species of grazers that assembled in large herds similar in size to those in Africa and Asia today. Species that roamed the great grasslands included the woolly mammoth, woolly rhino, steppe wisent, Lena Horse, muskox, and reindeer.

Another herbivore that was abundant in this region during the Pleistocene but now faces possible extinction in its remaining habitats is the saiga antelope, which can form massive herds that keep the vegetation down.

At the edges of these large stretches of grassland could be found more shrub-like terrain and dry conifer forests (similar to taiga). In this terrain the browsers of the Pleistocene were to be found. This group of megafauna included woolly rhinoceros, moose, wapiti, Yukon wild ass, and camels. The more mountainous terrain was occupied by several species of mountain-going animals like the snow sheep.

During the Pleistocene there was a great variety of carnivorous mammals as well. On the plains there were prides of Beringian cave lion. These large cats were the apex predators of the region, but also shared their habitat with other predators such as grey wolf, cave hyena, Homotherium, brown bear, wolverine, and Arctic fox, which all occupied a distinct ecological niche essential for the balance of their respective ecosystems.

On the edges of the grasslands (in the shrubs and forests) there were also brown bears, wolverines, cave bears, lynxes, tigers, leopards, and red foxes. The Siberian tiger and Amur leopard occupied the southern part of the steppe biome and surviving populations are still found along the present Russian-Sino border in the Amur and Primorye regions.

Proposed procedure

In present-day Siberia only a few of the former species of megafauna are left; and their population density is extremely low, too low to affect the environment. To reach the desired effects, the density has to be raised artificially by fencing in and concentrating the existing large herbivores. A large variety of species is important as each species affects the environment differently and as the overall stability of the ecosystem increases with the variety of species (compare Biodiversity and ecological services). Their numbers will be raised by reintroducing species that became locally extinct (e.g., muskoxen). For species that became completely extinct, suitable replacements will be introduced if possible (e.g., wild Bactrian camels for the extinct Pleistocene camels of the genus Paracamelus). As the number of herbivores increases, the enclosure will be expanded.

While this is taking place, the effects will be monitored. This concerns for example the effects on the flora (are the mosses being replaced by grasses, etc.), the effects on the atmosphere (changes in levels of methane, carbon dioxide, water vapor) and the effects on the permafrost.

Finally, once a high density of herbivores over a vast area has been reached, predators larger than the wolves will have to be introduced to keep the megafauna in check.

Progress and plans

1988–1996

The first grazing experiments began in 1988 at the Northeast Science Station in Chersky with Yakutian horses.

1996–2004

In 1996 a 50 ha (125 acre) enclosure was built in Pleistocene Park. As a first step in recreating the ancient landscape, the Yakutian horses were introduced, as horses had been the most abundant ungulates on the northeastern Siberian mammoth steppe. Of the first 40 horses, 15 were killed by predators and 12 died of eating poisonous plants. More horses were imported, and they learned to cope with the environment. In 2006 approximately 20 horses lived in the park, and by 2007 more horses were being born annually than died. By 2013, the number had risen to about 30. Moose, already present in the region, were also introduced. The effects of large animals (mammoths and wisents) on nature were artificially created by using an engineering tank and an 8 wheel drive Argo all-terrain vehicle to crush pathways through the willow shrub.

Restored grasslands in Pleistocene Park

The vegetation in the park started to change. In the areas where the horses grazed, the soil has been compacted and mosses, weeds and willow shrub were replaced by grasses. Flat grassland is now the dominating landscape inside the park. The permafrost was also influenced by the grazers. When air temperature sank to −40 °C (−40 °F) in winter, the temperature of the ground was found to be only –5 °C (+23 °F) under an intact cover of snow, but −30 °C (−22 °F) where the animals had trampled down the snow. The grazers thus help keep permafrost intact, thereby lessening the amount of methane released by the tundra.

2004–2011

In the years 2004–2005 a new fence was erected, creating an enclosure of 16 km2 (6 sq mi).

The new enclosure finally allowed a more rapid development of the project. After the fence was completed, reindeer were brought into the park from herds in the region and are now the most numerous ungulates in the park. To increase moose density in the park, special constructions were added to the fence in several places that allow animals outside the fenced area to enter the park, while not allowing them to leave. Besides that, wild moose calves were caught in other regions and transported to the park.

In 2007 a 32 meter (105 foot) high tower was erected in the park that constantly monitors the levels of methane, carbon dioxide and water vapor in the park's atmosphere.

In September 2010, 6 male muskox from Wrangel Island were reintroduced, but 2 muskoxen died in the first months: one from unknown causes, and the other from infighting among the muskoxen. Seven months later, in April 2011, 6 Altai wapiti and 5 wisents arrived at the park, the wapiti were from the Altai mountains and the wisents from Prioksko-Terrasny Nature Reserve, near Moscow. The enclosing fence proved too low for the wapiti, and by the end of 2012 all 6 had jumped the fence and run off.

2011–2016

In the years 2011–2016 progress slowed down as most energy was put into the construction of a 150 ha (370 ac) branch of Pleistocene Park near the city of Tula in Tula Oblast in Europe, see below (Wild Field section). A few more reindeer and moose were introduced into Pleistocene Park during this time, and a monitoring system for measuring the energy balance (ratio of energy emission and energy absorption) of the pasture was installed.

2017–present

Attention has now been shifted back to the further development of Pleistocene Park. A successful crowdfunding effort in early 2017 provided funding for further animal acquisitions. Later that year 12 domestic yak and 30 domestic sheep were brought to the park. and the introduction of more muskoxen was planned for 2020.

For the near future the focus in animal introductions will generally be placed on browsers, not grazers, i.e., bison, muskoxen, horses, and domestic yaks. Their role in this phase will be to diminish the amount of shrubs and trees and enlarge the grassy areas. Only when these areas have sufficiently increased will grazers like saiga and wild Bactrian camels be introduced.

Reception

Controversial aspects

Critics admonish that introducing alien species could damage the fragile ecosystem of the existing tundra. To this criticism Sergey Zimov replied: "The tundra is not an ecosystem. Such systems had not existed on the planet [before the disappearance of the megafauna], and there is nothing to cherish in the tundra. Of course, it would be silly to create a desert instead of the tundra, but if the same site would evolve into a steppe, then it certainly would improve the environment. If deer, foxes, bovines were more abundant, nature would only benefit from this. And people too. However, the danger still exists, of course, you have to be very careful. If it is a revival of the steppes, then, for example, small animals are really dangerous to release without control. As for large herbivores – no danger, as they are very easy to remove again."

Another point of concern is doubt that the majority of species can be introduced in such harsh conditions. For example, according to some critics, the Yakutian horses, although they have been living in the park for several generations, would not have survived without human intervention. They normally tolerate –60 °C, but are said to cope poorly with an abundance of snow and possibly would have died of starvation in the first snowy winter. However, horses of much less primitive stock abandoned by the Japanese Army have been living feral on some uninhabited Kuril Islands since 1945. Despite the deep snows (two to three times deeper than in Yakutia), they have successfully survived all the winters without feeding. And in Pleistocene Park, while some of the Yakutian horses accept supplementary feeding, others keep away and survive on their own.

Positive reception

The Zimovs' concept of Pleistocene Park and repopulating the mammoth steppe is listed as one of the “100 most substantive solutions to global warming” by Project Drawdown. The list, encompassing only technologically viable, existing solutions, was compiled by a team of over 200 scholars, scientists, policymakers, business leaders and activists; for each solution the carbon impact through the year 2050, the total and net cost to society, and the total lifetime savings were measured and modelled.

In January 2020, a study co-authored by Nikita Zimov and three University of Oxford researchers assessed the viability of the park's goals when implemented on a larger scale. It was estimated that if three large-scale experimental areas were set up, each containing 1000 animals and costing 114 million US dollars over a ten year period, that 72,000 metric tons of carbon could be held and generate 360,000 US dollars in carbon revenues. 

Visitors

The park is a hub for international scientists and students, who come from around the world to conduct their own ecological research and experiments. The Polaris Project was a yearly visitor from 2009 to 2015, sending American students on excursions to the park each summer.

Another group of visitors are journalists. The park is steadily gaining more media attention and while most journalists do not come to the park itself the number of visitors is increasing. In 2016 for example, the park was visited by a filmmaker, two print media (Swiss 24 Heures and American The Atlantic), and two TV broadcasting companies (German ARD and American HBO).

The total of visitors for 2016 (summer months only) was 45.

Size and administration

Pleistocene Park is a 160 km2 scientific nature reserve (zakaznik) consisting of willow brush, grasslands, swamps, forests and a multitude of lakes. The average temperature in January is about –33 °C and in July +12 °C; annual precipitation is 200–250 mm.

Pleistocene Park is owned and administered by a non-profit corporation, the Pleistocene Park Association, consisting of the ecologists from the Northeast Science Station in Chersky and the Grassland Institute in Yakutsk. The present park area was signed over to the association by the state and is exempt from land tax. The reserve is surrounded by a 600 km2 buffer zone that will be added to the park by the regional government once the animals have successfully established themselves.

In July 2015 the "Pleistocene Park Foundation". was founded, a non-profit organization (registered in Pennsylvania, USA, with 501(c)(3) status) dedicated to acquiring private donations for funding Pleistocene Park. Hitherto Pleistocene Park had been financed solely through the funds of the founders, a practice that grew increasingly insufficient.

In 2019 the "Pleistocene & Permafrost Foundation". was founded in Germany by Michael Kurzeja and Bernd Zehentbauer and serves as a bridge between science, politics, companies, and society. It takes care of the project's financing, seeks donations in kind such as tractors, utility vehicles, and pick-ups to build the park, and funds further research projects with the Max Planck Institute. "Dirk Steffens". and "Anabel Ternès". are involved as ambassadors.

Animals

Animals already present in the park

Herbivores

  • Reindeer (Rangifer tarandus): Present before the project started (although more are being brought to help simulate Pleistocene conditions). They mainly graze in the southern highlands of the park. This territory is not affected by spring flooding and dominated by larch forests and shrubland. Reindeer rarely visit the flood plain. Besides actively grazing (especially in winter) they browse on willow shrubs, tree moss, and lichens. (Numbers in park in November 2021: 20–30)
  • Elk[BE]/moose[AE] (Alces alces): Present before the project started, although in low numbers. Immigration from neighboring areas is stimulated. Due to poaching the density of moose in the region has substantially decreased in the last 20 years. To increase moose density in the park, special constructions were added to the fence in several places that allow animals outside the fenced area to enter the park, while not allowing them to leave. Besides that, wild moose calves are being caught in other regions and transported to the park. It is the largest extant species of the deer family and one of the largest herbivores in the park today. (Numbers in park in November 2021: 5–15)
  • Yakutian horse (a domestic breed of horse): The first species to be introduced for the project, they were imported from the surrounding Srednekolymsk region beginning in 1988. Yakutian horses have developed a range of remarkable morphologic, metabolic and physiologic adaptions to the harsh environment of Siberia, including an extremely dense and long winter coat, a compact build, a metabolism adjusted to seasonal needs, and an increased production of antifreezing compounds. In summer they grow very large hooves, which they wear down in winter scraping away snow to get at food. Despite their size, they proved to be dominant over the wisents, who often fled from them. Yakutian horses are purely grazing animals – they eat only grass species and visit the park's forests only during the spring flood. In the spring of 2015, ten more Yakutian horses were acquired to increase genetic diversity. (Numbers in park in November 2021: approximately 40)
Muskoxen family
  • Muskox (Ovibos moschatus): Muskoxen arrived at the park in September 2010. They were brought from Wrangel Island (itself repopulated with animals from North America). They are doing well and are now fully grown. Unfortunately only males could be acquired, after an attempt to get both males and females was thwarted during the expedition when a polar bear broke the fence to eat one of them, and the Zimovs are now urgently looking for females. The introduction of more muskoxen was planned for 2019. (Numbers in park in November 2021: 3 males) A new expedition to go to Wrangel Island was planned to take place in late 2020, but ultimately cancelled due to various delays by the time they had the boats ready, including by the COVID-19 pandemic
  • Wisent (AKA European bison, Bison bonasus): During the last ice age, wisents were the most cold-adapted of the Bison species and thrived in the glacial grassland-steppe biome. Their dietary needs are very different from the American bison. Year-round 10% of their diet necessarily consists of trees and shrubs, and they will ignore their main forage (grasses, sedges and forbs) in favour of woody forage to reach this quota. Without supplementary feeding in winter, the yearly average may rise to 20% even in countries with mild winters. Five wisents, one adult male and four juvenile females, were introduced in the park in April 2011. The wisents were brought to the park from the Prioksko-Terrasny Nature Reserve near Moscow. The transportation was more complicated and took a longer time than originally thought, but all the animals recovered rapidly after the trip. Unfortunately, the wisents did not sufficiently acclimatize in the first months. They started to moult in November, when temperatures already were down to –30 °C (–35 °F) in Cherskii. The four juveniles died; only the adult bull survived. He is now fully acclimatized. (Numbers in park in November 2021: 1 male)
  • Domestic yak (Bos mutus grunniens): Ten domestic yaks acquired in Irkutsk Oblast were introduced in Pleistocene Park in June 2017; two calves were born a few days after the arrival. Another calf was born after that. Yaks are adapted to extreme cold, short growing seasons for grazing herbage, and rough grazing conditions with sedges and shrubby plants. Wild yaks once lived in western Beringia.
  • Edilbaevskaya sheep (a domestic breed of sheep): 30 domestic sheep acquired in Irkutsk Oblast were introduced in Pleistocene Park in October 2017. The sheep are from a breed that is adapted to the Siberian cold. They belong to the breed group of fat-tailed sheep; their fatty rump evolved to store fat as a reserve for lean seasons, analogous to a camel's humps. (Numbers in park in November 2021: 18)
  • Kalmykian cattle (a domestic breed of cattle adapted for the Mongolian steppe): A population was introduced to the park in October 2018. (Numbers in park in November 2021: 15)
  • Plains bison (Bison bison bison): Twelve yearling plains bison, nine males and three females, were acquired and would have been introduced in the park once the United States’ FAA gave clearance for the flight. The plains bison were bought from the Stevens Village Bison Reserve near Delta Junction in Alaska; as the climate there is comparable to that of Siberia, the young bison were expected to thrive. Plains bison are grazers of grasses and sedges. Unlike wisents, plains bison are almost pure grazers, which will consume other plant material mainly in time of need. While wood bison were the preferred choice of subspecies, they are not easy to acquire; plains bison simply are the subspecies that could be brought to the Park most easily. They got bison from Denmark, from the Ditlevsdal bison farm. The bison began travelling on 7 May, and officially arrived safely in the park on 9 June. A second expedition to the Ditlevsdal bison farm allowed for another herd to be brought to the park. (Numbers in park in November 2021: 24)
  • Orenburg fur goat (Capra aegagrus hircus): Its presence is necessary due to their ability to eat anything, including plant poisonous to other herbivores. Only difficulty with acquiring them is due to them being only found in Orenburg, due to veterinary services not allowing shipping out of that region. Current plans involve bringing the goats from a farm belonging to a park ranger that formerly worked for Pleistocene Park into the park around May 2021. The trip to acquire them began on May 5, with the goats being loaded on May 8, then the long trek to bring them to Pleistocene Park finished with their arrival at the park on June 18. (Numbers in park in November 2021: 35)
  • Bactrian camel (Camelus bactrianus): Either of the two-humped camel species could act as a proxy for extinct Pleistocene camel species, whose fossils have been found in areas that once formed part of Beringia. The camel evolved in the high arctic as a large boreal browser; its hump presumably evolved to store fat as a resource for the long winter. Bactrian camels will eat almost anything, preferably any plant material such as grass, shrubs, bark, etc., but in times of need also carrion. In the winter they will dig under snow to get at forage. Camels are not suitable for wet environments, preferring uplands, and are mainly sought out in order to browse away at plants like willow shrubs, though they do sometimes eat the wet grasses. Domesticated Bactrian camels are currently set to be brought to the park around May 2021 from a farm in Orsk. The trip to acquire them began on May 5, with the camels being loaded on May 8, and then the expedition would wrap up with the transport truck carrying the camels arriving at Pleistocene Park on June 18. (Numbers in park in November 2021: 10)
  • Several non-ungulate herbivores were already present before establishment of the park and remain resident; these include the mountain hare (Lepus timidus), the black-capped marmot (Marmota camtschatica), the Arctic ground squirrel (Spermophilus parryii), the muskrat (Ondatra zibethicus), and diverse species of voles.

Carnivores

  • Eurasian lynx (Lynx lynx): Resident before the project started. It is an important predator of medium-sized herbivores like hares and roe deer.
  • Tundra wolf (Canis lupus albus): Before the project started the area was already home to a family of wolves, despite the originally low concentration of prey ungulates. This arctic subspecies of the gray wolf is widespread from northern Scandinavia to the Kamchatka Peninsula.
  • Arctic fox (Vulpes lagopus): Resident before the project started. Well adapted to living in the arctic environment, its fur changes color with the season: white in winter, brown in summer.
  • Eurasian brown bear (Ursus arctos arctos): Resident before the project started. Currently the largest predator in the region.
  • Wolverine (Gulo gulo): Present before the project started. A stocky and muscular carnivore, the wolverine is a powerful and versatile predator and scavenger.
  • Red fox (Vulpes vulpes): Resident before the project started. Red foxes are omnivores with a highly varied diet. From research conducted in the former Soviet Union, they are known to consume up to 300 animal species, mostly rodents and small lagomorphs, and a few dozen plant species.
  • Sable (Martes zibellina): Resident before the project started.
  • Stoat (Mustela erminea): Resident before the project started.

Animals considered for reintroduction

Herbivores

  • Altai wapiti or Altai maral (Cervus canadensis sibiricus): Had been introduced in April 2011. The wapiti made their way to the park all the way from the mountainous regions of Altai in central southern Siberia. Wapiti are very good jumpers and all six escaped within the first two years. The fence has been strengthened to cope with future introductions.
  • Wild yak (Bos mutus): Could be brought from the Tibetan Plateau. Along with the bison, horse, and reindeer, the species could contribute to the further proliferation of grasses in the region.
  • Snow sheep (Ovis nivicola): Immigration from neighboring areas is encouraged. Especially rams may be lured to the park by domestic ewes in rut.
  • Wild Bactrian camel (Camelus ferus): Like the domesticated Bactrian camel, could act as a proxy for extinct Pleistocene camel species, whose fossils have been found in areas that once formed part of Beringia. The wild Bactrian camel is critically endangered and is only found in some few areas of China and Mongolia.
  • Siberian roe deer (Capreolus pygargus): Immigration from neighboring areas is encouraged.
  • Saiga antelope (Saiga tatarica): Introduction is in the planning stage. Its presence would be critical for the regulation of poisonous plants in the region that can be digested by the saiga but are harmful to other herbivores. Currently, free saigas can only be found in Russia in the Chyornye Zemli Nature Reserve.

Carnivores

  • Siberian tiger (Panthera tigris tigris): Introduction planned for a later stage, when herbivores have multiplied. Endangered and reduced to the Primorye region. As the largest feline alive, the Siberian tiger could play a key role in regulating the numbers of the largest herbivores.

Animals that could be placed in the park if revived from extinction

  • Woolly mammoth (Mammuthus primigenius): In January 2011, the Yomiuri Shimbun reported that a team of scientists from Kyoto University were planning to extract DNA from a mammoth carcass preserved in a Russian laboratory and insert it into egg cells of Asian elephants in hope of creating a mammoth embryo. If the experiment succeeded, the calf would be taken to the park along with others to form a wild population. The researchers claimed that their aim was to produce the first mammoth within six years.
  • Cave lion (Panthera spelaea): The discovery of two well-preserved cubs in the Sakha Republic ignited a project to clone the animal.
  • Steppe bison (Bison priscus): The discovery of the mummified steppe bison of 9,000 years ago could help people clone the ancient bison species back, even though the steppe bison would not be the first to be "resurrected".
  • Woolly rhinoceros (Coelodonta antiquitatis): Similar reasons of bringing back as the woolly mammoth.
  • Irish elk (Megaloceros giganteus)
  • Cave bear (Ursus spelaeus

Southern branch of Pleistocene Park: The Wild Field wilderness reserve

In 2012 to 2014 a branch of Pleistocene Park named "Wild Field" (Russian: Дикое поле, Dikoe pole) was constructed near the city of Tula in Tula Oblast in the European part of Russia, approximately 250 km (150 mi) south of Moscow.

Unlike Pleistocene Park, Wild Field's primary purpose is not scientific research but public outreach, i.e., it will provide a model of what an unregulated steppe ecosystem looked like before the advent of humans. It is situated near a federal road and a railway station and will be accessible to the general public.

Wild Field comprises 300 ha (740 ac) of which 280 ha have been fenced off and stocked with animals. Already present in the park are nine species of large herbivores and one omnivore species: Bashkir horses (a strain of Equus ferus caballus) from the southern part of the Ural Mountains, Altai maral/Altai wapiti (Cervus canadensis sibiricus), Edilbaevskaya sheep (a strain of Ovis orientalis aries), roe deer (Capreolus spec.), Kalmykian cattle (a strain of Bos primigenius taurus), domestic yaks (Bos mutus grunniens), wild boar (Sus scrofa), one female elk/moose (Alces alces), four reindeer (Rangifer tarandus) and 73 domestic Pridonskaya goats (a strain of Capra aegagrus hircus).

Equus (genus)

From Wikipedia, the free encyclopedia
Equus
Temporal range: 5.33–0 Ma Earliest Pliocene to recent
Equus species.jpg
Clockwise (from top left): kiang (E. kiang), Przewalski's horse (E. ferus przewalskii), Grévy's zebra (E. grevyi), domestic horse (E. f. caballus), onager (E. hemionus), plains zebra (E. quagga), donkey (E. africanus asinus) and mountain zebra (E. zebra)
Scientific classification e
Kingdom: Animalia
Phylum: Chordata
Class: Mammalia
Order: Perissodactyla
Family: Equidae
Tribe: Equini
Genus: Equus
Linnaeus, 1758
Type species
Equus caballus
Linnaeus, 1758
Extant species

Equus (/ˈɛkwəs, ˈkwəs/) is a genus of mammals in the family Equidae, which includes horses, donkeys, and zebras. Within the Equidae, Equus is the only recognized extant genus, comprising seven living species. Like Equidae more broadly, Equus has numerous extinct species known only from fossils. The genus most likely originated in North America and spread quickly to the Old World. Equines are odd-toed ungulates with slender legs, long heads, relatively long necks, manes (erect in most subspecies), and long tails. All species are herbivorous, and mostly grazers, with simpler digestive systems than ruminants but able to subsist on lower-quality vegetation.

While the domestic horse and donkey (along with their feral descendants) exist worldwide, wild equine populations are limited to Africa and Asia. Wild equine social systems are in two forms; a harem system with tight-knit groups consisting of one adult male or stallion, several females or mares, and their young or foals; and a territorial system where males establish territories with resources that attract females, which associate very fluidly. In both systems, females take care of their offspring, but males may play a role as well. Equines communicate with each other both visually and vocally. Human activities have threatened wild equine populations.

Etymology

The word equus is Latin for "horse" and is cognate with the Greek ἵππος (hippos, "horse") and Mycenaean Greek i-qo /ikkʷos/, the earliest attested variant of the Greek word, written in Linear B syllabic script. Compare the alternative development of the Proto-Greek labiovelar in Ionic ἴκκος (ikkos).

Taxonomic and evolutionary history

The genus Equus was first described by Carl Linnaeus in 1758. It is the only recognized extant genus in the family Equidae. The first equids were small, dog-sized mammals (e.g. Eohippus) adapted for browsing on shrubs during the Eocene, around 54 million years ago (Mya). These animals had three toes on the hind feet and four on the front feet with small hooves in place of claws, but also had soft pads. Equids developed into larger, three-toed animals (e.g. Mesohippus) during the Oligocene and Miocene. From there, the side toes became progressively smaller through the Pleistocene until the emergence of the single-toed Equus.

The genus Equus, which includes all extant equines, is believed to have evolved from Dinohippus, via the intermediate form Plesippus. One of the oldest species is Equus simplicidens, described as zebra-like with a donkey-like head shape. The oldest material to date was found in Idaho, USA. The genus appears to have spread quickly into the Old World, with the similarly aged E. livenzovensis documented from western Europe and Russia. Molecular phylogenies indicate that the most recent common ancestor of all modern equines (members of the genus Equus) lived ~5.6 (3.9-7.8) Mya. Direct paleogenomic sequencing of a 700,000-year-old middle Pleistocene horse metapodial bone from Canada implies a more recent 4.07 Mya for the most recent common ancestor within the range of 4.0 to 4.5 Mya.

Mitochondrial evidence supports the division of Equus species into noncaballoid (which includes zebras and asses) and caballoids or "true horses" (which includes E. ferus and E. przewalskii). Of the extant equine species, the lineage of the asses may have diverged first, possibly as soon as Equus reached the Old World. Zebras appear to be monophyletic and differentiated in Africa, where they are endemic. Members of the subgenus Sussemionus were abundant during the Early and Middle Pleistocene of North America and Afro-Eurasia, but only a single species, E. ovodovi survived into the Late Pleistocene and Holocene in south Siberia and China, with the youngest remains from China dating to around 3500 BP (1500 BC), during the Shang dynasty. Genetic data from E. ovodovi has placed the Sussemionus lineage as closer to zebras and asses than to caballine horses.

Molecular dating indicates the caballoid lineage diverged from the noncaballoids 4 Mya. Genetic results suggest that all North American fossils of caballine equines, as well as South American fossils traditionally placed in the subgenus E. (Amerhippus), belong to E. ferus. Remains attributed to a variety of species and lumped together as New World stilt-legged horses (including E. francisci, E. tau, and E. quinni) probably all belong to a second species that was endemic to North America. This was confirmed in a genetic study done in 2017, which subsumed all the specimens into the species E. francisci which was placed outside all extant horse species in the new genus Haringtonhippus, although its placement as a separate genus was subsequently questioned. A separate genus of horse, Hippidion existed in South America. The possible causes of the extinction of horses in the Americas (about 12,000 years ago) have been a matter of debate. Hypotheses include climatic change and overexploitation by newly arrived humans. Horses only returned to the American mainland with the arrival of the conquistadores in 1519.

Prehistoric species

Many extinct prehistoric species of Equus have been described. The validity of some of these species is questionable and a matter of debate. For example, Equus niobrarensis is likely synonymous with Equus scotti, while Equus alaskae is most likely the same species as Equus lambei, which itself may be a North American form of the living Equus przewalskii.

DNA studies on American horse remains found frozen into permafrost have shown that several of the supposed American species, and the European Equus ferus, are actually one highly-variable widespread species. , as if the evolutionary process of speciation was persistently being frustrated by large herds of the horses moving long distances and mixing, carrying their genes about with them.

A mule (horse and donkey hybrid)

Domestic species

Hybrids

Equine species can crossbreed with each other. The most common hybrid is the mule, a cross between a male donkey and a female horse. With rare exceptions, these hybrids are sterile and cannot reproduce. A related hybrid, a hinny, is a cross between a male horse and a female donkey. Other hybrids include the zorse, a cross between a zebra and a horse and a zonkey or zedonk, a hybrid of a zebra and a donkey. In areas where Grévy's zebras are sympatric with plains zebras, fertile hybrids do occur. Ancient DNA identifies the Bronze Age kunga as a cross between the Syrian wild ass and the donkey.

Biology

Physical characteristics

From left to right: a cranium, a complete skeleton, a left forefoot frontal, and a left forefoot lateral from a Grévy's zebra

Equines have significant differences in size, though all are characterized by long heads and necks. Their slender legs support their weight on one digit (which evolved from the middle digits). Grévy's zebra is the largest wild species, standing up to 13.2 hands (54 inches, 137 cm) and weighing up to 405 kg (890 lb). Domesticated horses have a wider range of sizes. Heavy or draft horses are usually at least 16 hands (64 inches, 163 cm) high and can be as tall as 18 hands (72 inches, 183 cm) and weigh from about 700 to 1,000 kg (1,500 to 2,200 lb). Some miniature horses are no taller than 30 inches (76 cm) in adulthood. Sexual dimorphism is limited in equines. The penis of the male is vascular and lacks a bone (baculum). Equines are adapted for running and traveling over long distances. Their dentition is adapted for grazing; they have large incisors that clip grass blades and highly crowned, ridged molars well suited for grinding. Males have spade-shaped canines ("tushes"), which can be used as weapons in fighting. Equines have fairly good senses, particularly their eyesight. Their moderately long, erect ears are movable and can locate the source of a sound.

A dun-colored coat with primitive markings that include a dorsal stripe and often leg striping and transverse shoulder stripes reflect the wildtype coat and are observed in most wild extant equine species. Only the mountain zebra lacks a dorsal stripe. In domestic horses, dun color and primitive markings exist in some animals across many breeds. The purpose of the bold black-and-white striping of zebras has been a subject of debate among biologists for over a century, but 2014 evidence supports the theory that they are a form of protection from biting flies. These insects appear to be less attracted to striped coats, and compared to other wild equines, zebras live in areas with the highest fly activity. With the exception of the domestic horses, which have long manes that lay over the neck and long tail hair growing from the top of the tailhead or dock, most equines have erect manes and long tails ending in a tuft of hair. The coats of some equine species undergo shedding in certain parts of their range and are thick in the winter.

Ecology and daily activities

Group of onagers grazing

Extant wild equines have scattered ranges across Africa and Asia. The plains zebra lives in lush grasslands and savannas of Eastern and Southern Africa, while the mountain zebra inhabits mountainous areas of southwest Africa. The other equine species tend to occupy more arid environments with more scattered vegetation. Grévy's zebra is found in thorny scrubland of East Africa, while the African wild ass inhabits rocky deserts of North Africa. The two Asian wild ass species live in the dry deserts of the Near East and Central Asia and Przwelski's wild horse's habitat is the deserts of Mongolia. Only the range of the plains and Grévy's zebras overlap. In addition to wild populations, domesticated horses and donkeys are widespread due to humans. In certain parts of the world, populations of feral horses and feral donkeys exist, which are descended from domesticated animals that were released or escaped into the wild.

Equines are monogastric hindgut fermenters. They prefer to eat grasses and sedges, but may also consume bark, leaves, buds, fruits, and roots if their favored foods are scarce, particularly asses. Compared to ruminants, equines have a simpler and less efficient digestive system. Nevertheless, they can subsist on lower-quality vegetation. After food is passed through the stomach, it enters the sac-like cecum, where cellulose is broken down by micro-organisms. Fermentation is quicker in equines than in ruminants—30–45 hours for a horse compared to 70–100 hours for cattle. Equines may spend 60–80% of their time feeding, depending on the availability and quality of vegetation. In the African savannas, the plains zebra is a pioneer grazer, mowing down the upper, less nutritious grass canopy and preparing the way for more specialized grazers such as blue wildebeests and Thomson's gazelles, which depend on shorter and more nutritious grasses below.

Wild equines may spend seven hours a day sleeping. During the day, they sleep standing up, while at night they lie down. They regularly rub against trees, rocks, and other objects and roll in around in dust for protection against flies and irritation. Except the mountain zebra, wild equines can roll over completely.

Social behavior

Plains zebra group

Equines are social animals with two basic social structures.

Horses, plains zebras, and mountain zebras live in stable, closed family groups or harems consisting of one adult male, several females, and their offspring. These groups have their own home ranges, which overlap and they tend to be nomadic. The stability of the group remains even when the family stallion dies or is displaced. Plains zebra groups gather into large herds and may create temporarily stable subgroups within a herd, allowing individuals to interact with those outside their group. Among harem-holding species, this behavior has only otherwise been observed in primates such as the gelada and the hamadryas baboon. Females of harem species benefit as males give them more time for feeding, protection for their young, and protection from predators and harassment by outside males. Among females in a harem, a linear dominance hierarchy exists based on the time at which they join the group. Harems travel in a consistent filing order with the high-ranking mares and their offspring leading the groups followed by the next-highest ranking mare and her offspring, and so on. The family stallion takes up the rear. Social grooming (which involves individuals rubbing their heads against each other and nipping with the incisors and lips) is important for easing aggression and maintaining social bonds and status. Young of both sexes leave their natal groups as they mature; females are usually abducted by outside males to be included as permanent members of their harems.

In Grévy's zebras and the wild ass species, adults have more fluid associations and adult males establish large territories and monopolize the females that enter them. These species live in habitats with sparser resources and standing water, and grazing areas may be separated. Groups of lactating females are able to remain in groups with nonlactating ones and usually gather at foraging areas. The most dominant males establish territories near watering holes, where more sexually receptive females gather. Subdominants have territories farther away, near foraging areas. Mares may wander through several territories, but remain in one when they have young. Staying in a territory offers a female protection from harassment by outside males, as well as access to a renewable resource. Some feral populations of horses exhibit features of both the harem and territorial social systems.

In both equine social systems, excess males gather in bachelor groups. These are typically young males that are not yet ready to establish a harem or territory. With the plains zebra, the males in a bachelor group have strong bonds and have a linear dominance hierarchy. Fights between males usually occur over estrous females and involve biting and kicking.

Communication

When meeting for the first time or after they have separated, individuals may greet each other by rubbing and sniffing their noses followed by rubbing their cheeks, moving their noses along their bodies and sniffing each other's genitals. They then may rub and press their shoulders against each other and rest their heads on one another. This greeting is usually performed among harem or territorial males or among bachelor males playing.

Equines produce a number of vocalizations and noises. Loud snorting is associated with alarm. Squealing is usually made when in pain, but bachelors also squeal while play fighting. The contact calls of equines vary from the whinnying and nickering of the horse and the barking of plains zebras to the braying of asses, Grévy's zebras, and donkeys. Equines also communicate with visual displays, and the flexibility of their lips allows them to make complex facial expressions. Visual displays also incorporate the positions of the head, ears, and tail. An equine may signal an intention to kick by laying back its ears and sometimes lashing the tail. Flattened ears, bared teeth, and abrupt movement of the heads may be used as threatening gestures, particularly among stallions.

Reproduction and parenting

Grévy's zebra foal

Among harem-holding species, the adult females mate only with their harem stallion, while in other species, mating is more promiscuous and the males have larger testes for sperm competition. Estrus in female equines lasts 5–10 days; physical signs include frequent urination, flowing muscus, and swollen, everted labia. In addition, estrous females will stand with their hind legs spread and raise their tails when in the presence of a male. Males assess the female's reproductive state with the flehmen response and the female will solicit mating by backing in. Length of gestation varies by species; it is roughly 11–13 months, and most mares come into estrus again within a few days after foaling, depending on conditions. Usually, only a single foal is born, which is capable of running within an hour. Within a few weeks, foals attempt to graze, but may continue to nurse for 8–13 months. Species in arid habitats, like Grévy's zebra, have longer nursing intervals and do not drink water until they are three months old.

Among harem-holding species, foals are cared for mostly by their mothers, but if threatened by predators, the entire group works together to protect all the young. The group forms a protective front with the foals in the center and the stallion will rush at predators that come too close. In territory-holding species, mothers may gather into small groups and leave their young in "kindergartens" under the guard of a territorial male while searching for water. Grévy's zebra stallions may look after a foal in his territory to ensure that the mother stays, though it may not be his.

Human relations

Bronze Age pottery depicting horse and chariot

The earliest archaeological evidence for the domestication of the horse comes from sites in Ukraine and Kazakhstan, dating to around 4000–3500 BCE. By 3000 BCE, the horse was completely domesticated, and by 2000 BCE, a sharp increase occurred in the number of horse bones found in human settlements in northwestern Europe, indicating the spread of domesticated horses throughout the continent. The most recent, but most irrefutable, evidence of domestication comes from sites where horse remains were buried with chariots in graves of the Sintashta and Petrovka cultures c. 2100 BCE. Studies of variation in genetic material shows that a very few wild stallions, possibly all from a single haplotype, contributed to the domestic horse, mating with many mares in early domesticated herds.

Przewalski's horse has been conclusively shown not to be an ancestor of the domestic horse, though the two can hybridize and produce fertile offspring. The split between Przewalskii's horse and E. ferus caballus is estimated to have occurred 120,000–240,000 years ago, long before domestication. Of the caballine equines of E. ferus, E. f. ferus, also known as the European wild horse or "tarpan", shares ancestry with the modern domestic horse. In addition, tarpans that lived into modern times may have been hybridized with domestic horses.

Archaeological, biogeographical, and linguistic evidence suggests that the donkey was first domesticated by nomadic pastoral people in North Africa over 5,000 years ago. The animals were used to help cope with the increased aridity of the Sahara and the Horn of Africa. Genetic evidence finds that the donkey was domesticated twice based on two distinct mitochondrial DNA haplogroups. It also points to a single ancestor, the Nubian wild ass. Attempts to domesticate zebras were largely unsuccessful, though Walter Rothschild trained some to draw a carriage in England.

Conservation issues

Captive Przewalski's horse

Humans have had a great impact on the populations of wild equines. Threats to wild equines include habitat destruction and conflicts with local people and livestock. Since the 20th century, wild equines have been decimated over many of their former ranges and their populations scattered. In recent centuries, two subspecies, the quagga and the tarpan, became extinct. The IUCN lists the African wild ass as critically endangered, Grévy's zebra, the mountain zebra, and Przewalski's horse as endangered, the onager as vulnerable, the plains zebra as near threatened, and the kiang as least concern. Przewalski's horse was considered to be extinct in the wild from the 1960s to 1996. However, following successful captive breeding, it has been reintroduced in Mongolia.

Feral horses vary in degree of protection and generate considerable controversy. For example, in Australia, they are considered a non-native invasive species, often viewed as pests, though are also considered to have some cultural and economic value. In the United States, feral horses and burros are generally considered an introduced species because they are descendants from domestic horses brought to the Americas from Europe. While they are viewed as pests by many livestock producers, conversely, a view also exists that E. f. caballus is a reintroduced once-native species returned to the Americas that should be granted endangered species protection. At present, certain free-roaming horses and burros have federal protection as "living symbols of the historic and pioneer spirit of the West" under the Wild and Free-Roaming Horses and Burros Act of 1971, and in Kleppe v. New Mexico, the United States Supreme Court ruled that the animals so designated were, as a matter of law, wildlife.

Conservation of American bison

From Wikipedia, the free encyclopedia

The conservation of bison in North America is an ongoing, diverse effort to bring American bison (Bison bison) back from the brink of extinction. Plains bison, a subspecies (Bison bison bison), are a keystone species in the North American Great Plains. Bison are a species of conservation concern in part because they suffered a severe population bottleneck at the end of the 19th century. The near decimation of the species during the 1800s unraveled fundamental ties between bison, grassland ecosystems, and indigenous peoples’ cultures and livelihoods. English speakers used the word buffalo for this animal when they arrived. Bison was used as the scientific term to distinguish them from the true buffalo. Buffalo is commonly used as it continues to hold cultural significance, particularly for Indigenous people. Recovery began in the late 1800s with a handful of individuals independently saving the last surviving bison.# Dedicated restoration efforts in the 1900s bolstered bison numbers though they still exist in mostly small and isolated populations. Expansion of the understanding of bison ecology and management is ongoing. The contemporary widespread, collaborative effort includes attention to heritage genetics and minimal cattle introgression.

Context

Bison once roamed across most of North America in numbers that reached into the tens of millions. Before the 1800s, bison were a keystone species for the native shortgrass prairie habitat as their grazing pressure altered the food web and landscapes in ways that improve biodiversity. The expanses of grass sustained migrations of an estimated 30 to 60 million American bison which could be found across much of North America. While they ranged from the eastern seaboard states to southeast Washington, eastern Oregon, and northeastern California, the greatest numbers were found within the great bison belt on the shortgrass plains east of the Rocky Mountains that stretched from Alberta to Texas.

The grasslands once included more than 1,500 species of plants, 350 birds, 220 butterflies, and 90 mammals. The bison coexisted with elk, deer, pronghorn, swift fox, black-footed ferrets, black-tailed prairie dogs, white-tailed jackrabbits, bears, wolves, coyotes, and cougars. The bison scoring the trees with their horns kept them from taking over the open grasslands. As bison grazed, they dispersed seeds by excreting them. The heterogeneous or varied landscape created by the roaming bison helps birds and millions still arrive each year. Long-billed curlews are a migratory shorebirds that rely on three types of habitats on the prairie – areas with short grass, long grass and mud – for completing their breeding cycle each year. Mountain plovers use bison wallows as nesting sites. Prairie dogs benefited from the tendency of the bison to graze areas around prairie dog towns. The bison enjoyed the regrowth of plants previously cropped by the rodents which reduced the grass cover, making it easier to spot predators. Bald eagles, ravens, black-billed magpies, swift foxes, golden eagles, grizzly bears, wolves, beetles, and nematodes benefited from bison carcasses.

Such abundance made the bison a critical part of Native American culture: providing food as well as materials for clothing, shelter, tools, and more. As European Americans settled in the west in the 1800s, bison became the staple food for early explorers, fur traders, and many European settlers. As conflict with settlers developed, the U.S. Army began a campaign settle Native American tribes on the lands allotted to them. The country’s highest generals, politicians, and President Ulysses S. Grant saw the taking away their main food source by the destruction of buffalo as the best way to accomplish their removal from the landscape. Hundreds of thousands of bison were killed by U.S. troops and market hunters. The rapid slaughter of bison also surged when a tanning method was developed that allowed the soft hide to be made into tougher, more desirable leather that was sent to an international market. The transcontinental railroad was key in facilitating the large-scale hunting of bison along with the development of the repeating rifle.

Early efforts

In the late 1860s, private citizens independently began to capture and shelter bison. In 1874, both houses of Congress passed H.R. 921, To prevent the useless slaughter of buffaloes within the territories of the United States, but President Grant did not sign it, resulting in a pocket veto. By the late 1880s, the great herds of bison that once dominated the landscape were nearly gone. As they suffered a severe population bottleneck, bison became a species of conservation concern and various efforts to preserve the species through protection and stewardship began. The near decimation of the species unraveled fundamental ties between bison, grassland ecosystems, and Plains Indians’ cultures and livelihoods. As hunting ceased and private citizens provided grazing land, their ability of bison to increase their numbers was evident. As ranchers began to raise bison as livestock, they bred some of them with cattle. These bison-cattle hybridization experiments failed and were not repeated. Most of the bison available to establish conservation herds were from private herds resulting in cattle gene introgression being present in today's herds. Bison were for all practical purposes ecologically extinct across its former range, with multiple consequences for grassland biodiversity.

Oral accounts of the Confederated Salish and Kootenai tribes recall a man of the Pend d’Oreille tribe named Atatice who knew something needed to be done as the buffalo disappeared. Atatice’s son Latati, or Little Peregrine Falcon, eventually lead six orphan bison west to the Flathead Reservation. His stepfather, Samuel Walking Coyote, sold them to horse traders Michel Pablo and Charles Allard in 1884. The Pablo-Allard herd grew when in 1896 Allard died and his half of the herd was dispersed as it was sold to ranchers. Pablo’s herd continued to grow and range wild along the Flathead River. By the early 1900s, the Pablo-Allard herd was said to be the largest collection of the bison remaining in the U.S. Pablo was notified in 1904 that the government was opening up the Flathead Reservation for settlement by selling off parcels of land. After failed negotiations with the U.S. government, Pablo sold the herd to the Canadian government in 1907. The transfer took until 1912, as the bison were captured and shipped by train from Ravalli, Montana, to Elk Island to establish a conservation herd.

Bison grazing near Gibbon River at Madison in Yellowstone National Park.

Yellowstone National Park was established on March 1, 1872 where poaching of bison continued despite the presence of the First U.S. Cavalry soldiers at Fort Yellowstone to, in part, protect wildlife. Bison dwindled to about two dozen animals that spent winter in Pelican Valley. In May 1894, Congress passed the Act to Protect the Birds and Animals in Yellowstone National Park, and to Punish Crimes in Said Park. Known as the Lacey Act of 1894, the law provided punishment for poaching on public lands, resolved jurisdictional issues and helped Yellowstone's managers to start recovering the bison population. In 1902, they purchased 21 bison from private owners and raised them in Mammoth and then at the Lamar Buffalo Ranch.

Several bison first lived on the National Mall in a pen behind the Smithsonian Castle from 1888 until they were moved to the National Zoological Park that was established in 1891. Taxidermist William Temple Hornaday brought them back after he was sent out to collect bison specimens for the Smithsonian Museum in 1886. When he saw that bison were on the verge of extinction, his mission changed from hunting bison for display to preserving them in the wild. The American Bison Society (ABS) was formed in 1905 with Hornaday as its president to support bison recovery efforts. Theodore Roosevelt, named honorary president of the society, used his position as U.S. President to help the New York Zoological Society and the American Bison Society secure land, procure buffalo from ranchers and promote bison reintroduction projects. One of the first three bison restoration projects supported by Roosevelt and the ABS was the National Bison Range which returned some of the Allard herd to the Flathead Valley. The other two were the Wichita Mountains Reserve and Wind Cave National Park. On October 11, 1907, six bulls and nine cows were shipped by rail from the New York Zoological Park to the Wichita National Forest and Game Preserve in Oklahoma. Comanche Chief Quanah Parker came to the train station in Cache where the crates were transferred to horse-drawn wagons and hauled 13 miles (21 km) to the preserve. The children, waiting in the groups of Comanche families, had never seen a bison. In 1913, ABS sent 14 bison from the New York Zoological Gardens to Wind Cave National Park which had been created on January 3, 1903 by legislation signed by Roosevelt. An additional six bison were sent to the park in 1916 from Yellowstone National Park. Congress was also compelled to establish public bison herds at Sully’s Hill National Game Preserve and Fort Niobrara National Wildlife Refuge.

The bison at Lamar Buffalo Ranch eventually began to mix with the free-roaming population in Yellowstone Park and by 1954, their numbers had grown to roughly 1,300 animals. Bison reproduce and survive at relatively high rates compared to many other large, wild mammals, so even as the population recovered Yellowstone managers limited its growth with frequent culling. A moratorium on culling, that began in 1969, resulted in the bison population increasing dramatically. Removals began again in 1991 and averaged 233 bison per year from 1991 through 2017 as wildlife officials tried to curb some of that rapid growth of 10 to 17 percent every year. Yearly guidelines were issued on how many bison should be removed. Many slaughtered bison were provided to Native American Indian tribes, relief agencies and contract sales. Some live bison were shipped to zoos, reservations and other parks.

Contemporary approach

The management of the Yellowstone National Park herd shifted away from husbandry practices during the latter half of the 20th century to restoring wild behaviors and allowing bison to move freely within the park. Preservation of the species' wild character is essential to bison conservation and is an important management strategy for conservation herds. This includes maintaining a mix of age and sex classes and allowing bison to interact naturally with the ecosystem. Conservation herds are in mostly small and isolated populations. Large herds on extensive landscapes where natural limiting factors are present with minimal human interaction are seen as the best method to achieve the full potential of bison. The current strategy promotes having a minimum herd size of 1,000. Expansion of the understanding of bison ecology and management is ongoing.

A widespread, collaborative effort has led to the establishment of bison herds that include attention to heritage genetics and minimal cattle introgression. Tribal, federal, state, and non-governmental organizations conservation herds are managed with a focus on protecting wild bison and preserving their genetic diversity. Breeding efforts and genetic testing are used to develop herds that are relatively free of any detectable genetic material that would have come from cross-breeding with cattle. Scientific studies show that most bison conservation herds possess some small amounts of cattle genes. While mitochondrial DNA can potentially influence the cellular physiology of bison, a large majority of heritable traits seen are coded by chromosomal DNA---the structure containing most of the DNA in an organism. The presence of both mitochondrial DNA and minimal levels of chromosomal DNA may have insignificant influence on the reproductive processes and phenotypic expression of a bison herd. Many of these herds with genetic diversity are considered valuable for the conservation of the species. Brucellosis was first identified in Yellowstone bison in 1917 having been identified in domestic cattle in the United States in 1910. Introduced by European cattle, it infected wild elk and bison. The potential spread of the disease is an impediment to the recovery efforts. Other impediments include the nomadic behavior of wild herds, and legal jurisdiction.

The development of conservation biology included the restoration of ecological processes with an emphasis on the impact upon the ecosystem beyond the importance of the bison at the level of an individual species. The grazing of bison is important to soil, vegetation and overall ecological balance. Prairie ecosystems were maintained by a pattern of disturbance caused by natural wildfire and grazing by bison, a pattern which is called pyric herbivory. Before the 1800s, bison were a keystone species for the native shortgrass prairie habitat as their grazing pressure altered the food web and landscapes in ways that improve biodiversity. Ecocultural bison conservation concurrently pursued species conservation, restoration of ecological processes, and support of the traditional human use of natural resources. An ecocultural approach addresses the unique historical connection between bison and indigenous peoples, and the iconic status of bison for Canada and the United States. Many tribes and First Nations seek to establish and manage their own bison herds, to rescue and sustain cultural practices and sacred rituals, promote food security, and nourish cultural identity.

US Department of the Interior Bison Conservation Initiative

The US Department of the Interior (DOI) is the principal conservation agency of the United States and is responsible for the majority of the nationally owned public lands as well as its natural and cultural resources The DOI manages approximately one third of North America's bison in conservation herds. The National Park Service (NPS), US Fish and Wildlife Service (USFWS), and Bureau of Land Management (BLM) lands support appropriately 11,000 bison in 19 herds across 12 states. Together with the Bureau of Indian Affairs and the US Geological Survey, these DOI agencies promote bison conservation and shared stewardship. The 2008 issuance of the Bison Conservation Initiative (BCI) chartered the DOI Bison Working Groupon (BWG), an interagency group comprising representatives of the National Park Service, U.S. Fish and Wildlife Service, Bureau of Land Management, Bureau of Indian Affairs, and the U.S. Geological Survey. The Bison Conservation Initiative (BCI) was updated and adopted in May 2020. BWG, in conserving bison as wildlife, manages bison around principles and practices that maintain the wild character of bison, minimizes artificial selection, and allows forces of natural selection to operate, including competition for breeding. Using a metapopulation management strategy maintains genetic diversity and integrity through an interagency, science-based approach to restore gene flow across DOI bison conservation herds. The DOI works with conservation partners, states, tribes, nations, and non-governmental organizations (NGOs), to maintain large, wide-ranging, multi-jurisdictional bison herds on appropriate large landscapes.

Three free-ranging herds are managed by the National Park Service in the Grand Canyon, Grand Tetons, and Yellowstone national parks. Yellowstone National Park is the only place in the United States where bison have lived continuously since prehistoric times. The Grand Tetons and Yellowstone herds have minimal cattle gene introgression but are not disease-free. The Grand Canyon herd is disease free but has known cattle gene introgression.

Many of the conservation herds overseen directly by the Interior Department are small and spatially-constrained with fences with only the slightest traces of cattle interbreeding. The herds that have 400 or fewer animals are prone to problems of inbreeding and genetic drift that reduce environmental adaptability due to limited transfers for interbreeding among distant herds according to a 2019 study commissioned by the National Park Service.

Bison herds grow at a rate that rapidly outpaces the available habitat on DOI bison management units. Capture is periodically required to manage herd size and provides opportunities to donate live bison in support of partner conservation and restoration efforts. Low-stress handling practices reduce animal stress and increase safety for both bison and personnel during capture operations, while increasing overall alignment with the goal to manage bison as wildlife. BWG manages diseases in bison that may affect domestic livestock or other bison herds. Bison are donated to Native American tribes through tribal requests of parks or refuges or by way of the InterTribal Buffalo Council (ITBC). The ITBC is a federally recognized tribal organization that delivers live bison to member tribes, supports establishment of tribal bison herds, and supports the historical, cultural, traditional, and spiritual relationship of tribes and bison. Wind Cave National Park introduced 20 bison in 1913–16 and is routinely culled down to approximately 425. Theodore Roosevelt National Park introduced 29 animals to a South Unit in 1956 and subsequently transferred 20 bison from that herd to the park's North Unit in 1962. They are routinely culled down to approximately 350 and 20 animals, respectively. Badlands National Park introduced 53 animals in 1963–64 and another 20 in 1984 and is routinely culled down to approximately 700.

Greater Yellowstone Ecosystem

Bison grazing in Yellowstone

Only a few bull bison traversed outside Yellowstone National Park prior to 1975, but as bison numbers increased, groups of bison began migrating across the north and west boundaries of Yellowstone to expand their winter range and pioneer new territory in the Greater Yellowstone Ecosystem. Park and state wildlife officials went to great lengths to prevent bison from mixing with cattle. Brucellosis is known to exist in the elk and bison of the Yellowstone ecosystem. State and federal officials were pressured to prevent the spread of the disease as ranchers worry it could lead to Montana losing its brucellosis-free status. Montana state law does not allow the transport of wild bison exposed to brucellosis except to meat processing and research facilities within the state. State and federal officials rounded up most bison that wander outside the park every winter with up to 900 being removed annually. Some were captured and shipped to slaughter while others were shot by hunters or state agents. Montana managed a state-licensed hunt for bison that left the park from 1985 to 1991 but the number of bison migrating outside of the park continued to increase, prompting the National Park Service to develop management plans to control bison near the park boundaries. Intense controversy grew between environmentalists, livestock interests and agency managers.

During harsh winters, bison found convenient grazing on several U.S. Forest Service allotments that were used for cattle in the summer. In 1995, the Montana state legislature designated Yellowstone bison as a species in need of disease management and the state sued the National Park Service for allowing bison to leave the park. After five years of litigation and mediation, the state of Montana and the federal government developed the Interagency Bison Management Plan (IBMP) to guide the management of bison in and around Yellowstone. As part of this plan, five agencies and three tribal entities work to sustain a wild, wide-ranging bison population and reduce the risk of brucellosis transmission from bison to cattle. In the decades since the IBMP was created, the bison population has ranged between 2,400 and 5,500 animals. There have been no cases of bison transmitting brucellosis directly to cattle, in part due to efforts by federal and state agencies to maintain separation between these animals. The state of Montana now allows bison to occupy some habitat adjacent to the park that was previously off-limits, including year-round in some areas, which is a major conservation advancement. The lack of tolerance for wild bison in most areas outside Yellowstone continues to limit restoration. Large parts of their historic winter ranges are no longer available due to human development and states only allow limited numbers of bison in areas near the park. While hunting is not allowed within the park, it mainly occurs within an area outside the northern boundary near Gardiner as designated by the state. Removal numbers are decided each year, with tribal and state hunters being allowed a quota. Montana issues hunting permits and 4 tribes have long standing treaty rights to hunt Yellowstone bison. Most of the bison are sent to slaughter with the meat being distributed to participating tribes. The IBMP plan includes allowing bison to enter the Bison Conservation Transfer Program as space allows.

Bison Conservation Transfer Program

Yellowstone bison are exceptional because they comprise the nation's largest bison population on public land. Developing a quarantine program that complied with Montana state law was critical to getting brucellosis-free animals from Yellowstone to conservation herds. Quarantine was talked about in the 1990s during the negotiations on the IBMP. During 2005–2012, Animal and Plant Health Inspection Service (APHIS) developed and verified procedures for identifying Yellowstone bison that don't have brucellosis. Quarantine worked as bison that repeatedly tested negative for the disease stayed that way and could be certified as brucellosis-free. The initial plan was for the bison that completed the pilot program to be moved to public or tribal lands but the state was not ready to approve any of the proposed locations in 2010. After Montana Governor Brian Schweitzer invited Ted Turner to submit an offer to care for the animals, Turner Enterprises Inc. reached an agreement in February with the Montana Department of Fish, Wildlife and Parks to care for the bison and their offspring for five years on a 12,000-acre fenced section (4,900 ha) of the Flying D ranch. Tribal and state officials signed an agreement in 2012 allowing the transfer of bison that were also in the 2005-2012 pilot study. Sixty-three animals from the Yellowstone quarantine corrals were transferred in March to the Assiniboine and Sioux Tribes who started a conservation herd at their Fort Peck Reservation. A legal challenge blocked further transfers until the state supreme court ruled in June 2013 that the Montana law in question did not apply to tribal lands. The state was asked to move the bison by November 2014 that been regularly tested for brucellosis while being quarantined on behalf of the Montana Fish, Wildlife and Parks at the Bozeman-area ranch owned by Ted Turner. In October, the commission decided to move the animals to the Fort Peck Reservation as the commission recognized that the Fort Peck Fish and Game Department had done a good job of managing the bison including the disease testing. In November, 139 of the Yellowstone bison at the Flying D ranch joined the conservation herd at the Fort Peck Reservation.

Certification involves a multi-year process including holding animals in fenced pastures near the park boundary. The quarantine program approved by IBMP has three phases. First, bison are trapped at the Stephens Creek Bison Capture Facility where they are sorted by age and sex into different enclosed pens. A blood sample is also taken and they are tested for brucellosis with only about 30% of animals qualifying for the program. Bison that test negative can go into quarantine. Next, testing protocols continue until the animals can be certified as disease free. Finally, assurance testing involves another year in isolation with two more tests before the quarantine period is finished. The first two phases currently must be done in a supervised area in the vicinity of the park. APHIS and the Montana Department of Livestock established the final structural specifications and biosecurity requirements for quarantine facilities in June 2017. Two pens in a Yellowstone bison trap were made into quarantine corrals with two layers of fencing in 2017. The two facilities are located at Stephens Creek and Corwin Springs. Quarantine facilities are managed by APHIS who coordinates the transfers with the state of Montana and the Fort Peck tribes. The final phase of assurance testing can be performed at the Fort Peck Indian Reservation in northeastern Montana.

Tribes and First Nations

The Bison Conservation Transfer Program has allowed some captured bison that repeatedly test negative for brucellosis to provide disease-free bison with Yellowstone heritage genetics to tribes and First Nations. In addition to supporting cultural restoration, the quarantine program can support genetic conservation of DOI herds by incorporating Yellowstone-origin bison into the DOI metapopulation. The program is a partnership that includes Yellowstone National Park, the Assiniboine and Sioux Tribes of the Fort Peck Indian Reservation, APHIS, Montana Department of Livestock, the State of Montana, InterTribal Buffalo Council, Yellowstone Forever, Defenders of Wildlife and the Greater Yellowstone Coalition.

The InterTribal Buffalo Council (ITBC), as an advocates for tribal buffalo restoration, supported the construction of the quarantine facility at the Fort Peck Indian Reservation. They facilitate the transfer to tribes and First Nations who will use the bison to increase the genetic diversity and overall health of their own herds. The recipients must be members of ITBC and agree to have the animals managed for their genetics.

Under the new operational quarantine program, the first transfer into phase three at the Fort Peck Indian Reservation occurred in August 2019. The Assiniboine and Sioux Tribes would complete the quarantine program for 55 male bison who had been captured at Stephens Creek in the northwest corner of park in March 2018. Three males and 21 females captured at the same time remained in quarantine in corrals at Corwin Springs, just outside the park's North Entrance. By June 2020, 104 bison had been transferred to large corral specifically built for quarantining Yellowstone bison at the reservation. In August 2020, 40 buffalo, who had completed quarantine at the reservation, were distributed to 16 other tribes across the United States including Kansas, Wisconsin and Alaska. Since 2019, 294 bison have been transferred to the Fort Peck Tribes in northeastern Montana. Two family groups were transferred for the first time in December 2021.

Province and state programs

The Minnesota Bison Conservation Herd is a project of the Minnesota Department of Natural Resources (MDNR) to raise and manage a herd of bison with the healthiest genetics possible. The Minnesota Zoological Garden (MZG) manages the metapopulation with the MDNR using a strategy that maintains genetic diversity among the approximately 130 bison at four different locations: Blue Mounds State Park, Minneopa State Park, the Minnesota Zoo and Zollman Zoo. An ultimate herd size of 500 has been set to ensure the long-term sustainability of bison in Minnesota. Three free-ranging herds are managed by state wildlife agencies in Utah and Alaska. Montana Fish, Wildlife and Parks began researching re-establishing wild populations in 2010. The plan, which laid the groundwork for wild bison reintroduction without specifying any particular site or plan for a herd, was published in January 2020. The plan was ended under a settlement in a lawsuit by United Property Owners of Montana in 2021.

Internet research

From Wikipedia, the free encyclopedia https://en.wikipedia.org/wiki/Internet_...