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Wikipedia

Savanna

A savanna or savannah is a mixed woodland-grassland (i.e. grassy woodland) ecosystem characterised by the trees being sufficiently widely spaced so that the canopy does not close. The open canopy allows sufficient light to reach the ground to support an unbroken herbaceous layer consisting primarily of grasses.[1][2][3] According to Britannica, there exists four savanna forms; savanna woodland where trees and shrubs form a light canopy, tree savanna with scattered trees and shrubs, shrub savanna with distributed shrubs, and grass savanna where trees and shrubs are mostly nonexistent.[4]

A tree savanna in Tanzania, East Africa (Tarangire National Park)
A grass savannah in South Africa (Kruger National Park)

Savannas maintain an open canopy despite a high tree density.[5] It is often believed that savannas feature widely spaced, scattered trees. However, in many savannas, tree densities are higher and trees are more regularly spaced than in forests.[6][7][8][9] The South American savanna types cerrado sensu stricto and cerrado dense typically have densities of trees similar to or higher than that found in South American tropical forests,[6][8][9] with savanna ranging from 800 to 3300 trees per hectare (trees/ha) and adjacent forests with 800–2000 trees/ha. Similarly Guinean savanna has 129 trees/ha, compared to 103 for riparian forest,[7] while Eastern Australian sclerophyll forests have average tree densities of approximately 100 per hectare, comparable to savannas in the same region.[10]

Savannas are also characterised by seasonal water availability, with the majority of rainfall confined to one season; they are associated with several types of biomes, and are frequently in a transitional zone between forest and desert or grassland, though they're mostly a transition between desert to forest.[11] Savanna covers approximately 20% of the Earth's land area.[12] Unlike the prairies in North America and steppes in Eurasia, which would feature cold winters, savannahs are mostly located in areas having warm to hot climates, such as those in Africa, Australia, Thailand, South America and India.[13]

Etymology

The word derives from the Spanish sabana, which is itself a loanword from Taíno, which means "treeless grassland" in the West Indies.[14][15] The letter b in Spanish, when positioned in the middle of a word, is pronounced almost like an English v; hence the change of grapheme when transcribed into English.[16]

The word originally entered English as the Zauana in a description of the ilands of the kinges of Spayne from 1555.[17][19] This was equivalent in the orthography of the times to zavana (see history of V). Peter Martyr reported it as the local name for the plain around Comagre, the court of the cacique Carlos in present-day Panama. The accounts are inexact,[21] but this is usually placed in present-day Madugandí[22] or at points on the nearby Guna Yala coast opposite Ustupo[23] or on Point Mosquitos.[24] These areas are now either given over to modern cropland or jungle.[25]

Distribution

 
A savanna woodland in Northern Australia demonstrating the regular tree spacing characteristic of some savannas.

Many grassy landscapes and mixed communities of trees, shrubs, and grasses were described as savanna before the middle of the 19th century, when the concept of a tropical savanna climate became established. The Köppen climate classification system was strongly influenced by effects of temperature and precipitation upon tree growth, and his oversimplified assumptions resulted in a tropical savanna classification concept which resulted in it being considered as a "climatic climax" formation. The common usage meaning to describe vegetation now conflicts with a simplified yet widespread climatic concept meaning. The divergence has sometimes caused areas such as extensive savannas north and south of the Congo and Amazon Rivers to be excluded from mapped savanna categories.[26]

In different parts of North America, the word "savanna" has been used interchangeably with "barrens", "prairie", "glade", "grassland" and "oak opening".[27] Different authors have defined the lower limits of savanna tree coverage as 5–10% and upper limits range as 25–80% of an area. Two factors common to all savanna environments are rainfall variations from year to year, and dry season wildfires.[citation needed] In the Americas, e.g. in Belize, Central America, savanna vegetation is similar from Mexico to South America and to the Caribbean.[28] The distinction between woodland and savanna is vague and therefore the two can be combined into a single biome as both woodlands and savannas feature open-canopied trees with crowns not usually interlinking (mostly forming 25-60% cover).[14]

Over many large tropical areas, the dominant biome (forest, savanna or grassland) can not be predicted only by the climate, as historical events plays also a key role, for example, fire activity.[29] In some areas, indeed, it is possible for there to be multiple stable biomes.[30] The annual rainfall ranges from 500 mm (19.69 in) to 1,270 mm (50.00 in) per year, with the precipitation being more common in six or eight months of the year, followed by a period of drought. Savannas may at times be classified as forests.[13]

In climatic geomorphology it has been noted that many savannas occur in areas of pediplains and inselbergs.[31] It has been posited that river incision is not prominent but that rivers in savanna landscapes erode more by lateral migration.[31] Flooding and associated sheet wash have been prosposed as dominant erosion processes in savanna plains.[31]

Ecology

The savannas of tropical America comprises broadleaved trees such as Curatella, Byrsonima, and Bowdichia, with grasses such as Leersia and Paspalum. Bean relative Prosopis is common in the Argentinian savannahs. In the East African savannas, Acacia, Combretum, baobabs, Borassus, and Euphorbia are a common vegetation genera. Drier savannas there feature spiny shrubs and grasses, such as Andropogon, Hyparrhenia, and Themeda. Wetter savannas include Brachystegia trees and Pennisetum purpureum, and elephant grass type. West African savanna trees consist of Anogeissus, Combretum, and Strychnos. Indian savannas are mostly cleared, but the reserved ones feature Acacia, Mimosa, and Zizyphus over a grass cover comprising Sehima and Dichanthium. The Australian savannah is abundant with sclerophyllous evergreen vegetation, which include the eucalyptus, and as well as Acacia, Bauhinia, Pandanus with grasses such as Heteropogon and kangaroo grass (Themeda).[4]

Animals in the African savanna generally include the giraffe, elephant, buffalo, zebra, gnu, hippopotamus, rhinoceros, and antelope, where they rely on grass and/or tree foliage to survive. In the Australian savannah, mammals in the family Macropodidae predominate, such as kangaroos and wallabies, though cattle, horses, camels, donkeys and the Asian water buffalo, among others, have been introduced by humans.[4]

Threats

It is estimated that less than three percent of savanna ecosystems can be classified as highly intact.[32] Reasons for savanna degradation are manifold, as outlined below.

Changes in fire management

Savannas are subject to regular wildfires and the ecosystem appears to be the result of human use of fire. For example, Native Americans created the Pre-Columbian woodlands of North America by periodically burning where fire-resistant plants were the dominant species.[33] Aboriginal burning appears to have been responsible for the widespread occurrence of savanna in tropical Australia and New Guinea,[34] and savannas in India are a result of human fire use.[35] The maquis shrub savannas of the Mediterranean region were likewise created and maintained by anthropogenic fire.[36]

These fires are usually confined to the herbaceous layer and do little long term damage to mature trees. However, these fires either kill or suppress tree seedlings, thus preventing the establishment of a continuous tree canopy which would prevent further grass growth. Prior to European settlement aboriginal land use practices, including fire, influenced vegetation[37] and may have maintained and modified savanna flora.[3][34] It has been suggested by many authors[37][38] that aboriginal burning created a structurally more open savanna landscape. Aboriginal burning certainly created a habitat mosaic that probably increased biodiversity and changed the structure of woodlands and geographic range of numerous woodland species.[34][37] It has been suggested by many authors[38][39] that with the removal or alteration of traditional burning regimes many savannas are being replaced by forest and shrub thickets with little herbaceous layer.

The consumption of herbage by introduced grazers in savanna woodlands has led to a reduction in the amount of fuel available for burning and resulted in fewer and cooler fires.[40] The introduction of exotic pasture legumes has also led to a reduction in the need to burn to produce a flush of green growth because legumes retain high nutrient levels throughout the year, and because fires can have a negative impact on legume populations which causes a reluctance to burn.[41]

Grazing and browsing animals

 

The closed forest types such as broadleaf forests and rainforests are usually not grazed owing to the closed structure precluding grass growth, and hence offering little opportunity for grazing.[42] In contrast the open structure of savannas allows the growth of a herbaceous layer and is commonly used for grazing domestic livestock.[43] As a result, much of the world's savannas have undergone change as a result of grazing by sheep, goats and cattle, ranging from changes in pasture composition to woody weed encroachment.[44]

 
Iberian pigs feeding on acorns of an holm oak

The removal of grass by grazing affects the woody plant component of woodland systems in two major ways. Grasses compete with woody plants for water in the topsoil and removal by grazing reduces this competitive effect, potentially boosting tree growth.[45] In addition to this effect, the removal of fuel reduces both the intensity and the frequency of fires which may control woody plant species.[46] Grazing animals can have a more direct effect on woody plants by the browsing of palatable woody species. There is evidence that unpalatable woody plants have increased under grazing in savannas.[47] Grazing also promotes the spread of weeds in savannas by the removal or reduction of the plants which would normally compete with potential weeds and hinder establishment.[37] In addition to this, cattle and horses are implicated in the spread of the seeds of weed species such as prickly acacia (Acacia nilotica) and stylo (Stylosanthes species).[40] Alterations in savanna species composition brought about by grazing can alter ecosystem function, and are exacerbated by overgrazing and poor land management practices.

Introduced grazing animals can also affect soil condition through physical compaction and break-up of the soil caused by the hooves of animals and through the erosion effects caused by the removal of protective plant cover. Such effects are most likely to occur on land subjected to repeated and heavy grazing.[48] The effects of overstocking are often worst on soils of low fertility and in low rainfall areas below 500 mm, as most soil nutrients in these areas tend to be concentrated in the surface so any movement of soils can lead to severe degradation. Alteration in soil structure and nutrient levels affects the establishment, growth and survival of plant species and in turn can lead to a change in woodland structure and composition.

Tree clearing

 
Savanna in eastern South Africa
 
Savanna in Western Sydney

Large areas of Australian and South American savannas have been cleared of trees, and this clearing is continuing today. For example, until recently 480,000 ha of savanna were cleared annually in Australia alone primarily to improve pasture production.[37] Substantial savanna areas have been cleared of woody vegetation and much of the area that remains today is vegetation that has been disturbed by either clearing or thinning at some point in the past.

Clearing is carried out by the grazing industry in an attempt to increase the quality and quantity of feed available for stock and to improve the management of livestock. The removal of trees from savanna land removes the competition for water from the grasses present, and can lead to a two to fourfold increase in pasture production, as well as improving the quality of the feed available.[49] Since stock carrying capacity is strongly correlated with herbage yield, there can be major financial benefits from the removal of trees,[50] such as assisting with grazing management: regions of dense tree and shrub cover harbors predators, leading to increased stock losses, for example,[51] while woody plant cover hinders mustering in both sheep and cattle areas.[52]

A number of techniques have been employed to clear or kill woody plants in savannas. Early pastoralists used felling and girdling, the removal of a ring of bark and sapwood, as a means of clearing land.[53] In the 1950s arboricides suitable for stem injection were developed. War-surplus heavy machinery was made available, and these were used for either pushing timber, or for pulling using a chain and ball strung between two machines. These two new methods of timber control, along with the introduction and widespread adoption of several new pasture grasses and legumes promoted a resurgence in tree clearing. The 1980s also saw the release of soil-applied arboricides, notably tebuthiuron, that could be utilised without cutting and injecting each individual tree.

In many ways "artificial" clearing, particularly pulling, mimics the effects of fire and, in savannas adapted to regeneration after fire as most Queensland savannas are, there is a similar response to that after fire.[54] Tree clearing in many savanna communities, although causing a dramatic reduction in basal area and canopy cover, often leaves a high percentage of woody plants alive either as seedlings too small to be affected or as plants capable of re-sprouting from lignotubers and broken stumps. A population of woody plants equal to half or more of the original number often remains following pulling of eucalypt communities, even if all the trees over 5 metres are uprooted completely.

Exotic plant species

A number of exotic plants species have been introduced to the savannas around the world. Amongst the woody plant species are serious environmental weeds such as Prickly Acacia (Acacia nilotica), Rubbervine (Cryptostegia grandiflora), Mesquite (Prosopis spp.), Lantana (Lantana camara and L. montevidensis) and Prickly Pear (Opuntia spp.) A range of herbaceous species have also been introduced to these woodlands, either deliberately or accidentally including Rhodes grass and other Chloris species, Buffel grass (Cenchrus ciliaris), Giant rat's tail grass (Sporobolus pyramidalis) parthenium (Parthenium hysterophorus) and stylos (Stylosanthes spp.) and other legumes. These introductions have the potential to significantly alter the structure and composition of savannas worldwide, and have already done so in many areas through a number of processes including altering the fire regime, increasing grazing pressure, competing with native vegetation and occupying previously vacant ecological niches.[54][55] Other plant species include: white sage, spotted cactus, cotton seed, rosemary.

Climate change

Human induced climate change resulting from the greenhouse effect may result in an alteration of the structure and function of savannas. Some authors[56] have suggested that savannas and grasslands may become even more susceptible to woody plant encroachment as a result of greenhouse induced climate change. However, a recent case described a savanna increasing its range at the expense of forest in response to climate variation, and potential exists for similar rapid, dramatic shifts in vegetation distribution as a result of global climate change, particularly at ecotones such as savannas so often represent.[57]

Savanna ecoregions

 
Tropical savanna in Kenya.
 
Temperate savanna in New South Wales, Australia.
 
Mediterranean savanna in the Alentejo region, Portugal.
 
A montane savanna in the Colombian Andes.

A savanna can simply be distinguished by the open savannah, where grass prevails and trees are rare; and the wooded savannah, where the trees are densest, bordering an open woodland or forest. Specific savanna ecoregions of several different types include:

See also

References

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  2. ^ McPherson, G. R. (1997). Ecology and management of North American Savannas. Tucson, AZ: University of Arizona Press.
  3. ^ a b Werner, Patricia A.; B. H. Walker; P. A Stott (1991). "Introduction". In Patricia A. Werner (ed.). Savanna Ecology and Management: Australian Perspectives and Intercontinental Comparisons. Oxford: Blackwell Publishing. ISBN 978-0-632-03199-3.
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  60. ^ Angolan Scarp savanna and woodlands

External links

savanna, redirects, here, city, state, georgia, georgia, other, uses, disambiguation, savanna, savannah, mixed, woodland, grassland, grassy, woodland, ecosystem, characterised, trees, being, sufficiently, widely, spaced, that, canopy, does, close, open, canopy. Savannah redirects here For the city in the U S state of Georgia see Savannah Georgia For other uses see Savannah disambiguation A savanna or savannah is a mixed woodland grassland i e grassy woodland ecosystem characterised by the trees being sufficiently widely spaced so that the canopy does not close The open canopy allows sufficient light to reach the ground to support an unbroken herbaceous layer consisting primarily of grasses 1 2 3 According to Britannica there exists four savanna forms savanna woodland where trees and shrubs form a light canopy tree savanna with scattered trees and shrubs shrub savanna with distributed shrubs and grass savanna where trees and shrubs are mostly nonexistent 4 A tree savanna in Tanzania East Africa Tarangire National Park A grass savannah in South Africa Kruger National Park Savannas maintain an open canopy despite a high tree density 5 It is often believed that savannas feature widely spaced scattered trees However in many savannas tree densities are higher and trees are more regularly spaced than in forests 6 7 8 9 The South American savanna types cerrado sensu stricto and cerrado dense typically have densities of trees similar to or higher than that found in South American tropical forests 6 8 9 with savanna ranging from 800 to 3300 trees per hectare trees ha and adjacent forests with 800 2000 trees ha Similarly Guinean savanna has 129 trees ha compared to 103 for riparian forest 7 while Eastern Australian sclerophyll forests have average tree densities of approximately 100 per hectare comparable to savannas in the same region 10 Savannas are also characterised by seasonal water availability with the majority of rainfall confined to one season they are associated with several types of biomes and are frequently in a transitional zone between forest and desert or grassland though they re mostly a transition between desert to forest 11 Savanna covers approximately 20 of the Earth s land area 12 Unlike the prairies in North America and steppes in Eurasia which would feature cold winters savannahs are mostly located in areas having warm to hot climates such as those in Africa Australia Thailand South America and India 13 Contents 1 Etymology 2 Distribution 3 Ecology 4 Threats 4 1 Changes in fire management 4 2 Grazing and browsing animals 4 3 Tree clearing 4 4 Exotic plant species 4 5 Climate change 5 Savanna ecoregions 6 See also 7 References 8 External linksEtymologyThe word derives from the Spanish sabana which is itself a loanword from Taino which means treeless grassland in the West Indies 14 15 The letter b in Spanish when positioned in the middle of a word is pronounced almost like an English v hence the change of grapheme when transcribed into English 16 The word originally entered English as the Zauana in a description of the ilands of the kinges of Spayne from 1555 17 19 This was equivalent in the orthography of the times to zavana see history of V Peter Martyr reported it as the local name for the plain around Comagre the court of the cacique Carlos in present day Panama The accounts are inexact 21 but this is usually placed in present day Madugandi 22 or at points on the nearby Guna Yala coast opposite Ustupo 23 or on Point Mosquitos 24 These areas are now either given over to modern cropland or jungle 25 Distribution A savanna woodland in Northern Australia demonstrating the regular tree spacing characteristic of some savannas Many grassy landscapes and mixed communities of trees shrubs and grasses were described as savanna before the middle of the 19th century when the concept of a tropical savanna climate became established The Koppen climate classification system was strongly influenced by effects of temperature and precipitation upon tree growth and his oversimplified assumptions resulted in a tropical savanna classification concept which resulted in it being considered as a climatic climax formation The common usage meaning to describe vegetation now conflicts with a simplified yet widespread climatic concept meaning The divergence has sometimes caused areas such as extensive savannas north and south of the Congo and Amazon Rivers to be excluded from mapped savanna categories 26 In different parts of North America the word savanna has been used interchangeably with barrens prairie glade grassland and oak opening 27 Different authors have defined the lower limits of savanna tree coverage as 5 10 and upper limits range as 25 80 of an area Two factors common to all savanna environments are rainfall variations from year to year and dry season wildfires citation needed In the Americas e g in Belize Central America savanna vegetation is similar from Mexico to South America and to the Caribbean 28 The distinction between woodland and savanna is vague and therefore the two can be combined into a single biome as both woodlands and savannas feature open canopied trees with crowns not usually interlinking mostly forming 25 60 cover 14 Over many large tropical areas the dominant biome forest savanna or grassland can not be predicted only by the climate as historical events plays also a key role for example fire activity 29 In some areas indeed it is possible for there to be multiple stable biomes 30 The annual rainfall ranges from 500 mm 19 69 in to 1 270 mm 50 00 in per year with the precipitation being more common in six or eight months of the year followed by a period of drought Savannas may at times be classified as forests 13 In climatic geomorphology it has been noted that many savannas occur in areas of pediplains and inselbergs 31 It has been posited that river incision is not prominent but that rivers in savanna landscapes erode more by lateral migration 31 Flooding and associated sheet wash have been prosposed as dominant erosion processes in savanna plains 31 EcologyThe savannas of tropical America comprises broadleaved trees such as Curatella Byrsonima and Bowdichia with grasses such as Leersia and Paspalum Bean relative Prosopis is common in the Argentinian savannahs In the East African savannas Acacia Combretum baobabs Borassus and Euphorbia are a common vegetation genera Drier savannas there feature spiny shrubs and grasses such as Andropogon Hyparrhenia and Themeda Wetter savannas include Brachystegia trees and Pennisetum purpureum and elephant grass type West African savanna trees consist of Anogeissus Combretum and Strychnos Indian savannas are mostly cleared but the reserved ones feature Acacia Mimosa and Zizyphus over a grass cover comprising Sehima and Dichanthium The Australian savannah is abundant with sclerophyllous evergreen vegetation which include the eucalyptus and as well as Acacia Bauhinia Pandanus with grasses such as Heteropogon and kangaroo grass Themeda 4 Animals in the African savanna generally include the giraffe elephant buffalo zebra gnu hippopotamus rhinoceros and antelope where they rely on grass and or tree foliage to survive In the Australian savannah mammals in the family Macropodidae predominate such as kangaroos and wallabies though cattle horses camels donkeys and the Asian water buffalo among others have been introduced by humans 4 ThreatsIt is estimated that less than three percent of savanna ecosystems can be classified as highly intact 32 Reasons for savanna degradation are manifold as outlined below Changes in fire management Bushfire in Kakadu National Park Australia Savannas are subject to regular wildfires and the ecosystem appears to be the result of human use of fire For example Native Americans created the Pre Columbian woodlands of North America by periodically burning where fire resistant plants were the dominant species 33 Aboriginal burning appears to have been responsible for the widespread occurrence of savanna in tropical Australia and New Guinea 34 and savannas in India are a result of human fire use 35 The maquis shrub savannas of the Mediterranean region were likewise created and maintained by anthropogenic fire 36 These fires are usually confined to the herbaceous layer and do little long term damage to mature trees However these fires either kill or suppress tree seedlings thus preventing the establishment of a continuous tree canopy which would prevent further grass growth Prior to European settlement aboriginal land use practices including fire influenced vegetation 37 and may have maintained and modified savanna flora 3 34 It has been suggested by many authors 37 38 that aboriginal burning created a structurally more open savanna landscape Aboriginal burning certainly created a habitat mosaic that probably increased biodiversity and changed the structure of woodlands and geographic range of numerous woodland species 34 37 It has been suggested by many authors 38 39 that with the removal or alteration of traditional burning regimes many savannas are being replaced by forest and shrub thickets with little herbaceous layer The consumption of herbage by introduced grazers in savanna woodlands has led to a reduction in the amount of fuel available for burning and resulted in fewer and cooler fires 40 The introduction of exotic pasture legumes has also led to a reduction in the need to burn to produce a flush of green growth because legumes retain high nutrient levels throughout the year and because fires can have a negative impact on legume populations which causes a reluctance to burn 41 Grazing and browsing animals Grevy s zebras grazing The closed forest types such as broadleaf forests and rainforests are usually not grazed owing to the closed structure precluding grass growth and hence offering little opportunity for grazing 42 In contrast the open structure of savannas allows the growth of a herbaceous layer and is commonly used for grazing domestic livestock 43 As a result much of the world s savannas have undergone change as a result of grazing by sheep goats and cattle ranging from changes in pasture composition to woody weed encroachment 44 Iberian pigs feeding on acorns of an holm oak The removal of grass by grazing affects the woody plant component of woodland systems in two major ways Grasses compete with woody plants for water in the topsoil and removal by grazing reduces this competitive effect potentially boosting tree growth 45 In addition to this effect the removal of fuel reduces both the intensity and the frequency of fires which may control woody plant species 46 Grazing animals can have a more direct effect on woody plants by the browsing of palatable woody species There is evidence that unpalatable woody plants have increased under grazing in savannas 47 Grazing also promotes the spread of weeds in savannas by the removal or reduction of the plants which would normally compete with potential weeds and hinder establishment 37 In addition to this cattle and horses are implicated in the spread of the seeds of weed species such as prickly acacia Acacia nilotica and stylo Stylosanthes species 40 Alterations in savanna species composition brought about by grazing can alter ecosystem function and are exacerbated by overgrazing and poor land management practices Introduced grazing animals can also affect soil condition through physical compaction and break up of the soil caused by the hooves of animals and through the erosion effects caused by the removal of protective plant cover Such effects are most likely to occur on land subjected to repeated and heavy grazing 48 The effects of overstocking are often worst on soils of low fertility and in low rainfall areas below 500 mm as most soil nutrients in these areas tend to be concentrated in the surface so any movement of soils can lead to severe degradation Alteration in soil structure and nutrient levels affects the establishment growth and survival of plant species and in turn can lead to a change in woodland structure and composition Tree clearing Savanna in eastern South Africa Savanna in Western Sydney Large areas of Australian and South American savannas have been cleared of trees and this clearing is continuing today For example until recently 480 000 ha of savanna were cleared annually in Australia alone primarily to improve pasture production 37 Substantial savanna areas have been cleared of woody vegetation and much of the area that remains today is vegetation that has been disturbed by either clearing or thinning at some point in the past Clearing is carried out by the grazing industry in an attempt to increase the quality and quantity of feed available for stock and to improve the management of livestock The removal of trees from savanna land removes the competition for water from the grasses present and can lead to a two to fourfold increase in pasture production as well as improving the quality of the feed available 49 Since stock carrying capacity is strongly correlated with herbage yield there can be major financial benefits from the removal of trees 50 such as assisting with grazing management regions of dense tree and shrub cover harbors predators leading to increased stock losses for example 51 while woody plant cover hinders mustering in both sheep and cattle areas 52 A number of techniques have been employed to clear or kill woody plants in savannas Early pastoralists used felling and girdling the removal of a ring of bark and sapwood as a means of clearing land 53 In the 1950s arboricides suitable for stem injection were developed War surplus heavy machinery was made available and these were used for either pushing timber or for pulling using a chain and ball strung between two machines These two new methods of timber control along with the introduction and widespread adoption of several new pasture grasses and legumes promoted a resurgence in tree clearing The 1980s also saw the release of soil applied arboricides notably tebuthiuron that could be utilised without cutting and injecting each individual tree In many ways artificial clearing particularly pulling mimics the effects of fire and in savannas adapted to regeneration after fire as most Queensland savannas are there is a similar response to that after fire 54 Tree clearing in many savanna communities although causing a dramatic reduction in basal area and canopy cover often leaves a high percentage of woody plants alive either as seedlings too small to be affected or as plants capable of re sprouting from lignotubers and broken stumps A population of woody plants equal to half or more of the original number often remains following pulling of eucalypt communities even if all the trees over 5 metres are uprooted completely Exotic plant species Acacia savanna Taita Hills Wildlife Sanctuary Kenya A number of exotic plants species have been introduced to the savannas around the world Amongst the woody plant species are serious environmental weeds such as Prickly Acacia Acacia nilotica Rubbervine Cryptostegia grandiflora Mesquite Prosopis spp Lantana Lantana camara and L montevidensis and Prickly Pear Opuntia spp A range of herbaceous species have also been introduced to these woodlands either deliberately or accidentally including Rhodes grass and other Chloris species Buffel grass Cenchrus ciliaris Giant rat s tail grass Sporobolus pyramidalis parthenium Parthenium hysterophorus and stylos Stylosanthes spp and other legumes These introductions have the potential to significantly alter the structure and composition of savannas worldwide and have already done so in many areas through a number of processes including altering the fire regime increasing grazing pressure competing with native vegetation and occupying previously vacant ecological niches 54 55 Other plant species include white sage spotted cactus cotton seed rosemary Climate change Human induced climate change resulting from the greenhouse effect may result in an alteration of the structure and function of savannas Some authors 56 have suggested that savannas and grasslands may become even more susceptible to woody plant encroachment as a result of greenhouse induced climate change However a recent case described a savanna increasing its range at the expense of forest in response to climate variation and potential exists for similar rapid dramatic shifts in vegetation distribution as a result of global climate change particularly at ecotones such as savannas so often represent 57 Savanna ecoregions Tropical savanna in Kenya Temperate savanna in New South Wales Australia Mediterranean savanna in the Alentejo region Portugal Nile Delta flooded savanna A montane savanna in the Colombian Andes A savanna can simply be distinguished by the open savannah where grass prevails and trees are rare and the wooded savannah where the trees are densest bordering an open woodland or forest Specific savanna ecoregions of several different types include Tropical savannas are classified with tropical and subtropical grasslands and shrublands as the tropical and subtropical grasslands savannas and shrublands biome The savannas of Africa including the Serengeti famous for its wildlife are typical of this type The Brazilian savanna Cerrado is also included in this category known for its exotic and varied flora Other examples include the Kimberley tropical savanna Central Zambezian miombo woodlands Guinean forest savanna mosaic Cape York Peninsula tropical savanna Somali Acacia Commiphora bushlands and thickets Terai Duar savanna and grasslands and the Victoria Basin forest savanna mosaic Subtropical and temperate savannas are mid latitude savannas with wetter summers and drier winters They are classified with temperate savannas and shrublands as the temperate grasslands savannas and shrublands biome that for example cover much of the plains of southeastern Australia northern India Southern Africa southeastern Argentina and Uruguay Examples of subtropical and temperate savannas include the Southeast Australia temperate savanna Argentine Espinal Pampas Cumberland Plain Woodland Southern Cone Mesopotamian savanna New England Peppermint Grassy Woodland and the Uruguayan savanna Mediterranean savannas are mid latitude savannas in Mediterranean climate regions with mild rainy winters and hot dry summers part of the Mediterranean forests woodlands and scrub biome The oak tree savannas of California part of the California chaparral and woodlands ecoregion fall into this category including the Temperate Grassland of South Australia which features eucalyptuses Parts of the Middle East steppe and the Eastern Mediterranean conifer sclerophyllous broadleaf forests may also feature savannah like landscapes Flooded savannas are savannas that are flooded seasonally or year round They are classified with flooded savannas as the flooded grasslands and savannas biome which occurs mostly in the tropics and subtropics Examples include the Everglades Mesopotamian Marshes Pantanal Nile Delta flooded savanna Lake Chad flooded savanna Zambezian flooded grasslands and the Sudd Montane savannas are mid to high altitude savannas located in a few spots around the world s high mountain regions part of the montane grasslands and shrublands biome The Bogota savanna located at an average altitude of 2 550 metres 8 370 ft on the Altiplano Cundiboyacense Eastern Ranges of the Andes is an example of a montane savanna 58 59 The savannas of the Angolan Scarp savanna and woodlands ecoregion are a lower altitude example up to 1 000 metres 3 300 ft 60 Other examples include the Al Hajar montane woodlands and the southern part of the Eastern Anatolian montane steppe See alsoPampas Pasture Prairie Rangeland Steppe VeldReferences Anderson Roger A Fralish James S and Baskin Jerry M editors 1999 Savannas Barrens and Rock Outcrop Plant Communities of North America Cambridge University Press McPherson G R 1997 Ecology and management of North American Savannas Tucson AZ University of Arizona Press a b Werner Patricia A B H Walker P A Stott 1991 Introduction In Patricia A Werner ed Savanna Ecology and Management Australian Perspectives and Intercontinental Comparisons Oxford Blackwell Publishing ISBN 978 0 632 03199 3 a b c Smith Jeremy M B savanna Encyclopedia Britannica 5 Sep 2016 https www britannica com science savanna Environment Accessed 17 September 2022 Alexandro Solorzano Jeanine Maria Felfili 2008 Comparative analysis of the international terminaoolgy for cerrado IX Symposio Nacional Cerrado 13 a 17 de outubro de 2008 Parlamundi Barsilia DF a b Manoel Claudio da Silva Janior Christopher William Fagg Maria Cristina Felfili Paulo Ernane Nogueira Alba Valeria Rezende and Jeanine Maria Felfili 2006 Chapter 4 Phytogeography of Cerrado Sensu Stricto and Land System Zoning in Central Brazil in Neotropical Savannas and Seasonally Dry Forests Plant Diversity Biogeography and Conservation R Toby Pennington James A Ratter eds 2006 CRC Press a b Abdullahi Jibrin 2013 A Study of Variation in Physiognomic Characteristics of Guinea Savanna Vegetation Environment and Natural Resources Research 3 2 a b Erika L Geiger Sybil G Gotsch Gabriel Damasco M Haridasan Augusto C Franco amp William A Hoffmann 2011 Distinct roles of savanna and forest tree species in regeneration under fire suppression in a Brazilian savanna Journal of Vegetation Science 22 a b Scholz Fabian G Bucci Sandra J Goldstein Guillermo Meinzer Frederick C Franco Augusto C Salazar Ana 2008 Plant and stand level variation in biophysical and physiological traits along tree density gradients in the Cerrado Brazilian Journal of Plant Physiology Tait L 2010 Structure and dynamics of grazed woodlands in North eastern Australia Master of Applied Science Thesis Central Queensland University Faculty of Science Engineering and Health Rockhampton Savanna Ask a Biologist Retrieved 31 August 2022 Sankaran Mahesh Hanan Niall P Scholes Robert J Ratnam Jayashree Augustine David J Cade Brian S Gignoux Jacques Higgins Steven I Le Roux Xavier December 2005 Determinants of woody cover in African savannas Nature 438 7069 846 849 Bibcode 2005Natur 438 846S doi 10 1038 nature04070 ISSN 0028 0836 PMID 16341012 S2CID 4344778 a b The grassland biome UCMP Retrieved 31 August 2022 a b WOODLAND SAVANNA Wrangle WORLD RANGELAND LEARNING EXPERIENCE 2022 Arizona Board of Regents Retrieved 17 September 2022 ASALE RAE RAE macana Diccionario de la lengua espanola Diccionario de la lengua espanola Edicion del Tricentenario in Spanish Retrieved 18 November 2019 B A Seattle Pacific University How to Pronounce B and V in Spanish ThoughtCo Retrieved 29 August 2021 Oxford English Dictionary 3rd ed savannah n Oxford University Press Oxford 2012 a b D Anghiera Peter Martyr De Orbe Novo Decades Cum Ejusdem Legatione Babylonica The Decades of the New World With the Babylonian Legation Arnao Guillen de Brocar Alcala 1516 in Latin Trans Richard Eden as The decades of the newe worlde or west India conteynyng the nauigations and conquestes of the Spanyardes with the particular description of the moste ryche and large landes and Ilands lately founde in the west Ocean perteynyng to the inheritaunce of the kinges of Spayne Book III 3 William Powell London 1555 Richard Eden The palace of this Comogrus is ſituate at the foote of a ſtiepe hyll well cultured Hauynge towarde the ſouthe a playne of twelue leages in breadth and veary frutefull This playne they caule Zauana 18 Eden 1555 Book III 6 The account of Peter Martyr itself differs in places variously placing Comagre 25 leagues west of and accessible by ship from Dariena 20 or 70 leagues roughly 290 kilometers or 180 miles west of Dariena and beside a river flowing into the southern ocean 18 Bancroft Hubert H 1882 History of Central America 1501 1530 San Francisco A L Bancroft amp Co p LXXIV Bancroft 1882 p 362 Bancroft 1882 p 347 NASA earthobservatory nasa gov Experiments ICE panama Images igbp panama2000289 lg gif Land Cover Classification from Earth Observatory The Image Composite Explorer Exercise 4 Vegetation Vital Signs Accessed 1 August 2014 David R Harris ed 1980 Human Ecology in Savanna Environments London Academic Press pp 3 5 9 12 271 278 297 298 ISBN 978 0 12 326550 0 Roger C Anderson James S Fralish Jerry M Baskin eds 1999 Savannas Barrens and Rock Outcrop Plant Communities of North America Cambridge University Press p 157 ISBN 978 0 521 57322 1 David L Lentz ed 2000 Imperfect balance landscape transformations in the Precolumbian Americas New York City Columbia University Press pp 73 74 ISBN 978 0 231 11157 7 Moncrieff G R Scheiter S Langan L Trabucco A Higgins S I 2016 The future distribution of the savannah biome model based and biogeographic contingency Philos T R Soc B 371 2015 0311 2016 link Staver A C Archibald S Levin S A 2011 The global extent and determinants of savanna and forest as alternative biome states Science 334 230 232 link a b c Cotton C A 1961 The Theory of Savanna Planation Geography 46 2 89 101 JSTOR 40565228 Williams Brooke A Watson James E M Beyer Hawthorne L Grantham Hedley S Simmonds Jeremy S Alvarez Silvia J Venter Oscar Strassburg Bernardo B N Runting Rebecca K 1 December 2022 Global drivers of change across tropical savannah ecosystems and insights into their management and conservation Biological Conservation 276 109786 doi 10 1016 j biocon 2022 109786 ISSN 0006 3207 S2CID 253503609 Use of Fire by Native Americans The Southern Forest Resource Assessment Summary Report Southern Research Station USDA Forest Service Archived from the original on 5 March 2014 Retrieved 21 July 2008 a b c Flannery Timothy Fridtjof 1994 The Future Eaters An Ecological History of the Australasian Lands and People Frenchs Forest New South Wales Reed New Holland ISBN 978 0 8076 1403 7 Saha S 2003 Patterns in woody species diversity richness and partitioning of diversity in forest communities of tropical deciduous forest biomes Ecography 26 1 80 86 doi 10 1034 j 1600 0587 2003 03411 x Pyne Stephen J 1997 Vestal Fire An Environmental History Told through Fire of Europe and Europe s Encounter with the World Seattle University of Washington Press ISBN 978 0 295 97596 2 a b c d e Wilson B S Boulter et al 2000 Queensland s resources Native Vegetation Management in Queensland S L Boulter B A Wilson J Westrupet eds Brisbane Department of Natural Resources ISBN 0 7345 1701 7 a b Lunt I D N Jones 2006 Effects of European colonisation on indigenous ecosystems post settlement changes in tree stand structures in Eucalyptus Callitris woodlands in central New South Wales Australia Journal of Biogeography 33 6 1102 1115 doi 10 1111 j 1365 2699 2006 01484 x S2CID 85775764 Archer S 1994 Woody plant encroachment into southwestern grasslands and savannas Rates patterns and proximate causes pp 13 68 in Vavra Laycock and Pieper eds Ecological Implications of Livestock Herbivory in the West Society For Range Management Denver ISBN 1 884930 00 X a b Pressland A J J R Mills et al 1988 Landscape degradation in native pasture Native pastures in Queensland their resources and management W H Burrows J C Scanlan and M T Rutherford Queensland Queensland Government Press ISBN 0 7242 2443 2 Dyer R A Craig et al 1997 Fire in northern pastoral lands Fire in the management of northern Australian pastoral lands T C Grice and S M Slatter St Lucia Australia Tropical Grassland Society of Australia ISBN 0 9590948 9 X Lodge G M and R D B Whalley 1984 Temperate rangelands Management of Australia s Rangelands G N Harrington and A D Wilson Melbourne CSIRO Publishing Mott J J Groves R H 1994 Natural and derived grasslands Australian Vegetation R H Groves Cambridge Cambridge University Press Winter W H 1991 Australia s northern savannas a time for change in management philosophy In Patricia A Werner ed Savanna Ecology and Management Australian Perspectives and Intercontinental Comparisons Oxford Blackwell Publishing pp 181 186 ISBN 978 0 632 03199 3 Burrows W H J C Scanlan et al 1988 Plant ecological relations in open forests woodlands and shrublands Native pastures in Queensland their resources and management W H Burrows J C Scanlan and M T Rutherford eds Brisbane Department of Primary Industries ISBN 0 7242 2443 2 Smith G A Franks et al 2000 Impacts of domestic grazing within remnant vegetation Native Vegetation Management in Queensland S L Boulter B A Wilson J Westrupet al Brisbane Department of Natural Resources ISBN 0 7345 1701 7 Florence R G 1996 Ecology and silviculture of eucalypt forests Collingwood CSIRO Publishing ISBN 0 643 10252 3 Foran B D 1984 Central arid woodlands Management of Australia s Rangelands G N Harrington and A D Wilson Melbourne CSIRO Publishing ISBN 0 643 03615 6 Scanlan J and C Chilcott 2000 Management and production aspects Native Vegetation Management in Queensland S L Boulter B A Wilson J Westrupet al Brisbane Department of Natural Resources Harrington G N M H Friedel et al 1984 Vegetation ecology and management Management of Australia s Rangelands G N Harrington and A D Wilson Melbourne CSIRO Publishing ISBN 0 643 03615 6 Harrington G N D M D Mills et al 1984 Semi arid woodlands Management of Australia s Rangelands G N Harrington and A D Wilson Melbourne CSIRO Publishing ISBN 0 643 03615 6 Harrington G N D M D Mills et al 1984 Management of Rangeland Ecosystems Management of Australia s Rangelands G N Harrington and A D Wilson Melbourne CSIRO Publishing ISBN 0 643 03615 6 Partridge I 1999 Managing grazing in northern Australia Brisbane Department of Primary Industries ISBN 0 7345 0035 1 a b Scanlan J C 1988 Managing tree and shrub populations Native pastures in Queensland their resources and management W H Burrows J C Scanlan and M T Rutherford Queensland Queensland Government Press ISBN 0 7242 2443 2 Tothill J C and C Gillies 1992 The pasture lands of northern Australia Brisbane Tropical Grassland Society of Australia ISBN 0 9590948 4 9 Archer S 1991 Development and stability of grass woody mosaics in a subtropical savanna parkland Texas USA In Patricia A Werner ed Savanna Ecology and Management Australian Perspectives and Intercontinental Comparisons Oxford Blackwell Publishing pp 109 118 ISBN 978 0 632 03199 3 Allen C D amp D D Breshears 1998 Drought induced shift of a forest woodland ecotone Rapid landscape response to climate variation Proceedings of the National Academy of Sciences 95 25 14839 14842 Bibcode 1998PNAS 9514839A doi 10 1073 pnas 95 25 14839 PMC 24536 PMID 9843976 Calvachi Zambrano Byron 2002 La biodiversidad bogotana PDF Revista la Tadeo in Spanish Universidad Jorge Tadeo Lozano 67 89 98 Retrieved 4 March 2017 Perez Preciado Alfonso 2000 La estructura ecologica principal de la Sabana de Bogota PDF in Spanish Sociedad Geografica de Colombia pp 1 37 Retrieved 4 March 2017 Angolan Scarp savanna and woodlandsExternal links Wikimedia Commons has media related to Savannas The Savanna Savanna Encyclopaedia Britannica 11th ed 1911 Savannas New International Encyclopedia 1905 Retrieved from https en wikipedia org w index php title Savanna amp oldid 1126940923, wikipedia, wiki, book, books, library,

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