fbpx
Wikipedia

Old-growth forest

An old-growth forest[a] is a forest that has developed over a long period of time without disturbance. Due to this, old-growth forests exhibit unique ecological features.[1] The Food and Agriculture Organization of the United Nations defines primary forests as naturally regenerated forests of native tree species where there are no clearly visible indications of human activity and the ecological processes are not significantly disturbed. Barely one-third (34 percent) of the world's forests are primary forests.[2] Old-growth features include diverse tree-related structures that provide diverse wildlife habitats that increases the biodiversity of the forested ecosystem. Virgin or first-growth forests are old-growth forests that have never been logged. The concept of diverse tree structure includes multi-layered canopies and canopy gaps, greatly varying tree heights and diameters, and diverse tree species and classes and sizes of woody debris.

Old-growth European beech forest in Biogradska Gora National Park, Montenegro
Cool temperate rainforest in Tasmania, Australia
First growth or virgin forest near Mount Rainier

As of 2020, the world has 1.11 billion ha of primary forest remaining. Combined, three countries (Brazil, Canada, and Russia) host more than half (61 percent) of the world's primary forest. The area of primary forest has decreased by 81 million ha since 1990, but the rate of loss more than halved in 2010–2020 compared with the previous decade.[3]

Old-growth forests are valuable for economic reasons and for the ecosystem services they provide.[4][5] This can be a point of contention when some in the logging industry desire to harvest valuable timber from the forests, destroying the forests in the process, to generate short-term profits, while environmentalists seek to preserve the forests in their pristine state for benefits such as water purification, flood control, weather stability, maintenance of biodiversity, and nutrient cycling. Moreover, old-growth forests are more efficient at sequestering carbon than newly planted forests and fast-growing timber plantations, thus preserving the forests is important to climate change mitigation.[6][7]

Characteristics edit

 
Antarctic beech old-growth in Lamington National Park, Queensland, Australia

Old-growth forests tend to have large trees and standing dead trees, multilayered canopies with gaps that result from the deaths of individual trees, and coarse woody debris on the forest floor.[8]

A forest regenerated after a severe disturbance, such as wildfire, insect infestation, or harvesting, is often called second-growth or 'regeneration' until enough time passes for the effects of the disturbance to be no longer evident. Depending on the forest, this may take from a century to several millennia. Hardwood forests of the eastern United States can develop old-growth characteristics in 150–500 years. In British Columbia, Canada, old growth is defined as 120 to 140 years of age in the interior of the province where fire is a frequent and natural occurrence. In British Columbia's coastal rainforests, old growth is defined as trees more than 250 years, with some trees reaching more than 1,000 years of age.[9] In Australia, eucalypt trees rarely exceed 350 years of age due to frequent fire disturbance.[10]

Forest types have very different development patterns, natural disturbances and appearances. A Douglas-fir stand may grow for centuries without disturbance while an old-growth ponderosa pine forest requires frequent surface fires to reduce the shade-tolerant species and regenerate the canopy species.[11] In the boreal forest of Canada, catastrophic disturbances like wildfires minimize opportunities for major accumulations of dead and downed woody material and other structural legacies associated with old growth conditions.[12] Typical characteristics of old-growth forest include the presence of older trees, minimal signs of human disturbance, mixed-age stands, presence of canopy openings due to tree falls, pit-and-mound topography, down wood in various stages of decay, standing snags (dead trees), multilayered canopies, intact soils, a healthy fungal ecosystem, and presence of indicator species.[citation needed]

Biodiversity edit

 
The northern spotted owl primarily inhabits old-growth forests in the northern part of its range (Canada to southern Oregon) and landscapes with a mix of old and younger forest types in the southern part of its range (the Klamath region and California).

Old-growth forests are often biologically diverse, and home to many rare species, threatened species, and endangered species of plants and animals, such as the northern spotted owl, marbled murrelet and fisher, making them ecologically significant. Levels of biodiversity may be higher or lower in old-growth forests compared to that in second-growth forests, depending on specific circumstances, environmental variables, and geographic variables. Logging in old-growth forests is a contentious issue in many parts of the world. Excessive logging reduces biodiversity, affecting not only the old-growth forest itself, but also indigenous species that rely upon old-growth forest habitat.[13][14]

Mixed age edit

Some forests in the old-growth stage have a mix of tree ages, due to a distinct regeneration pattern for this stage. New trees regenerate at different times from each other, because each of them has a different spatial location relative to the main canopy, hence each one receives a different amount of light. The mixed age of the forest is an important criterion in ensuring that the forest is a relatively stable ecosystem in the long term. A climax stand that is uniformly aged becomes senescent and degrades within a relatively short time to result in a new cycle of forest succession. Thus, uniformly aged stands are less stable ecosystems. Boreal forests are more uniformly aged, as they are normally subject to frequent stand-replacing wildfires.

Canopy openings edit

Forest canopy gaps are essential in creating and maintaining mixed-age stands. Also, some herbaceous plants only become established in canopy openings, but persist beneath an understory. Openings are a result of tree death due to small impact disturbances such as wind, low-intensity fires, and tree diseases.

Old-growth forests are unique, usually having multiple horizontal layers of vegetation representing a variety of tree species, age classes, and sizes, as well as "pit and mound" soil shape with well-established fungal nets.[15] Because old-growth forest is structurally diverse, it provides higher-diversity habitat than forests in other stages. Thus, sometimes higher biological diversity can be sustained in old-growth forests, or at least a biodiversity that is different from other forest stages.

 
Virgin forest about 2500 m above sea level in Shennongjia Forestry District, Hubei, China

Topography edit

The characteristic topography of much old-growth forest consists of pits and mounds. Mounds are caused by decaying fallen trees, and pits (tree throws) by the roots pulled out of the ground when trees fall due to natural causes, including being pushed over by animals. Pits expose humus-poor, mineral-rich soil and often collect moisture and fallen leaves, forming a thick organic layer that is able to nurture certain types of organisms. Mounds provide a place free of leaf inundation and saturation, where other types of organisms thrive.[4]

Standing snags edit

Standing snags provide food sources and habitat for many types of organisms. In particular, many species of dead-wood predators such as woodpeckers must have standing snags available for feeding. In North America, the spotted owl is well known for needing standing snags for nesting habitat.[4]

Decaying ground layer edit

 
Downed wood replenishes topsoil as it decays.
 
Fungus Climacocystis borealis on a tree stump in the Białowieża Forest, one of the last largely intact primeval forests in Central Europe

Fallen timber, or coarse woody debris, contributes carbon-rich organic matter directly to the soil, providing a substrate for mosses, fungi, and seedlings, and creating microhabitats by creating relief on the forest floor. In some ecosystems such as the temperate rain forest of the North American Pacific coast, fallen timber may become nurse logs, providing a substrate for seedling trees.[4]

Soil edit

Intact soils harbor many life forms that rely on them. Intact soils generally have very well-defined horizons, or soil profiles. Different organisms may need certain well-defined soil horizons to live, while many trees need well-structured soils free of disturbance to thrive. Some herbaceous plants in northern hardwood forests must have thick duff layers (which are part of the soil profile). Fungal ecosystems are essential for efficient in-situ recycling of nutrients back into the entire ecosystem.[4]

Definitions edit

Ecological definitions edit

Stand age definition edit

Stand age can also be used to categorize a forest as old-growth.[16] For any given geographical area, the average time since disturbance until a forest reaches the old growth stage can be determined. This method is useful, because it allows quick and objective determination of forest stage. However, this definition does not provide an explanation of forest function. It just gives a useful number to measure. So, some forests may be excluded from being categorized as old-growth even if they have old-growth attributes just because they are too young. Also, older forests can lack some old-growth attributes and be categorized as old-growth just because they are so old. The idea of using age is also problematic, because human activities can influence the forest in varied ways. For example, after the logging of 30% of the trees, less time is needed for old-growth to come back than after removal of 80% of the trees. Although depending on the species logged, the forest that comes back after a 30% harvest may consist of proportionately fewer hardwood trees than a forest logged at 80% in which the light competition by less important tree species does not inhibit the regrowth of vital hardwoods.

Forest dynamics definition edit

From a forest dynamics perspective, old-growth forest is in a stage that follows understory reinitiation stage.[17] A review of the stages helps to understand the concept:

  1. Stand-replacing: Disturbance hits the forest and kills most of the living trees.
  2. Stand-initiation: A population of new trees becomes established.
  3. Stem-exclusion: Trees grow higher and enlarge their canopy, thus competing for the light with neighbors; light competition mortality kills slow-growing trees and reduces forest density, which allows surviving trees to increase in size. Eventually, the canopies of neighboring trees touch each other and drastically lower the amount of light that reaches lower layers. Due to that, the understory dies and only very shade-tolerant species survive.
  4. Understory reinitiation: Trees die from low-level mortality, such as windthrow and diseases. Individual canopy gaps start to appear and more light can reach the forest floor. Hence, shade-tolerant species can establish in the understory.
  5. Old-growth: Main canopy trees become older and more of them die, creating even more gaps. Since the gaps appear at different times, the understory trees are at different growth stages. Furthermore, the amount of light that reaches each understory tree depends on its position relative to the gap. Thus, each understory tree grows at a different rate. The differences in establishment timing and in growth rate create a population of understory trees that is variable in size. Eventually, some understory trees grow to become as tall as the main canopy trees, thereby filling the gap. This perpetuation process is typical for the old-growth stage. This, however, does not mean that the forest will be old-growth forever. Generally, three futures for old-growth stage forest are possible: 1) The forest will be hit by a disturbance and most of the trees will die, 2) Unfavorable conditions for new trees to regenerate will occur. In this case, the old trees will die and smaller plants will create woodland, and 3) The regenerating understory trees are different species from the main canopy trees. In this case, the forest will switch back to stem-exclusion stage, but with shade-tolerant tree species. 4) The forest in an old-growth stage can be stable for centuries, but the length of this stage depends on the forest's tree composition and the climate of the area. For example, frequent natural fires do not allow boreal forests to be as old as coastal forests of western North America.

Of importance is that while the stand switches from one tree community to another, the stand will not necessarily go through old-growth stage between those stages. Some tree species have a relatively open canopy. That allows more shade-tolerant tree species to establish below even before the understory reinitiation stage. The shade-tolerant trees eventually outcompete the main canopy trees in stem-exclusion stage. Therefore, the dominant tree species will change, but the forest will still be in stem-exclusion stage until the shade-tolerant species reach old-growth stage.

Tree species succession may change tree species' composition once the old-growth stage has been achieved. For example, an old boreal forest may contain some large aspen trees, which may die and be replaced by smaller balsam fir or black spruce. Consequently, the forest will switch back to understory reinitiation stage.[18] Using the stand dynamics definition, old-growth can be easily evaluated using structural attributes. However, in some forest ecosystems, this can lead to decisions regarding the preservation of unique stands or attributes that will disappear over the next few decades because of natural succession processes. Consequently, using stand dynamics to define old-growth forests is more accurate in forests where the species that constitute old-growth have long lifespans and succession is slow.[4]

Social and cultural definitions edit

 
Redwood tree in northern California redwood forest: According to the National Park Service, "96 percent of the original old-growth coast redwoods have been logged."[19]

Common cultural definitions and common denominators regarding what comprises old-growth forest, and the variables that define, constitute and embody old-growth forests include:

  • The forest habitat possesses relatively mature, old trees;
  • The tree species present have long continuity on the same site;
  • The forest itself is a remnant natural area that has not been subjected to significant disturbance by mankind, altering the appearance of the landscape and its ecosystems, has not been subjected to logging (or other types of development such as road networks or housing), and has inherently progressed per natural tendencies.

Additionally, in mountainous, temperate landscapes (such as Western North America), and specifically in areas of high-quality soil and a moist, relatively mild climate, some old-growth trees have attained notable height and girth (DBH: diameter at breast height), accompanied by notable biodiversity in terms of the species supported. Therefore, for most people, the physical size of the trees is the most recognized hallmark of old-growth forests, even though the ecologically productive areas that support such large trees often comprise only a very small portion of the total area that has been mapped as old-growth forest.[20] (In high-altitude, harsh climates, trees grow very slowly and thus remain at a small size. Such trees also qualify as old growth in terms of how they are mapped, but are rarely recognized by the general public as such.)

The debate over old-growth definitions has been inextricably linked with a complex range of social perceptions about wilderness preservation, biodiversity, aesthetics, and spirituality, as well as economic or industrial values.[12][21]

Economic definitions edit

In logging terms, old-growth stands are past the economic optimum for harvesting—usually between 80 and 150 years, depending on the species. Old-growth forests were often given harvesting priority[clarification needed] because they had the most commercially valuable timber, they were considered to be at greater risk of deterioration through root rot or insect infestation, and they occupied land that could be used for more productive second-growth stands.[22] In some regions, old growth is not the most commercially viable timber—in British Columbia, Canada, harvesting in the coastal region is moving to younger second-growth stands.[23]

Other definitions edit

A 2001 scientific symposium in Canada found that defining old growth in a scientifically meaningful, yet policy-relevant, manner presents some basic difficulties, especially if a simple, unambiguous, and rigorous scientific definition is sought. Symposium participants identified some attributes of late-successional, temperate-zone, old-growth forest types that could be considered in developing an index of "old-growthness" and for defining old-growth forests:[24]

Structural features:

 
Avatar Grove near Port Renfrew, British Columbia: Giant Douglas firs (left) and red cedars (right) fill the grove.
  • Uneven or multi-aged stand structure, or several identifiable age cohorts
  • Average age of dominant species approaching half the maximum longevity for species (about 150+ years for most shade-tolerant trees)
  • Some old trees at close to their maximum longevity (ages of 300+ years)
  • Presence of standing dead and dying trees in various stages of decay
  • Fallen, coarse woody debris
  • Natural regeneration of dominant tree species within canopy gaps or on decaying logs

Compositional features:

  • Long-lived, shade-tolerant tree species associations (e.g., sugar maple, American beech, yellow birch, red spruce, eastern hemlock, white pine)

Process features:

  • Characterized by small-scale disturbances creating gaps in the forest canopy
  • A long natural rotation for catastrophic or stand-replacing disturbance (e.g., a period greater than the maximum longevity of the dominant tree species)
  • Minimal evidence of human disturbance
  • Final stages of stand development before a relatively steady state is reached

Importance edit

 
Eucalyptus regnans forest in Tasmania, Australia
  • Old-growth forests often contain rich communities of plants and animals within the habitat due to the long period of forest stability. These varied and sometimes rare species may depend on the unique environmental conditions created by these forests.
  • Old-growth forests serve as a reservoir for species, which cannot thrive or easily regenerate in younger forests, so they can be used as a baseline for research.
  • Plant species that are native to old-growth forests may someday prove to be invaluable towards curing various human ailments, as has been realized in numerous plants in tropical rainforests.[25][26]
  • Old-growth forests also store large amounts of carbon above and below the ground (either as humus, or in wet soils as peat). They collectively represent a very significant store of carbon. Destruction of these forests releases this carbon as greenhouse gases, and may increase the risk of global climate change.[27] Although old-growth forests serve as a global carbon dioxide sink, they are not protected by international treaties, because it is generally thought that aging forests cease to accumulate carbon. However, in forests between 15 and 800 years of age, net ecosystem productivity (the net carbon balance of the forest including soils) is usually positive; old-growth forests accumulate carbon for centuries and contain large quantities of it.[28]

Ecosystem services edit

Old-growth forests provide ecosystem services that may be far more important to society than their use as a source of raw materials. These services include making breathable air, making pure water, carbon storage, regeneration of nutrients, maintenance of soils, pest control by insectivorous bats and insects, micro- and macro-climate control, and the storage of a wide variety of genes.[29][30]

Climatic impacts edit

The effects of old-growth forests in relation to global warming have been addressed in various studies and journals.

The Intergovernmental Panel on Climate Change said in its 2007 report: "In the long term, a sustainable forest management strategy aimed at maintaining or increasing forest carbon stocks, while producing an annual sustained yield of timber, fibre, or energy from the forest, will generate the largest sustained mitigation benefit."[7]

Old-growth forests are often perceived to be in equilibrium or in a state of decay.[31] However, evidence from analysis of carbon stored above ground and in the soil has shown old-growth forests are more productive at storing carbon than younger forests.[6] Forest harvesting has little or no effect on the amount of carbon stored in the soil,[32] but other research suggests older forests that have trees of many ages, multiple layers, and little disturbance have the highest capacities for carbon storage.[33] As trees grow, they remove carbon from the atmosphere, and protecting these pools of carbon prevents emissions into the atmosphere. Proponents of harvesting the forest argue the carbon stored in wood is available for use as biomass energy (displacing fossil fuel use),[34] although using biomass as a fuel produces air pollution in the form of carbon monoxide, nitrogen oxides, volatile organic compounds, particulates, and other pollutants, in some cases at levels above those from traditional fuel sources such as coal or natural gas.[35][36][37]

Each forest has a different potential to store carbon. For example, this potential is particularly high in the Pacific Northwest where forests are relatively productive, trees live a long time, decomposition is relatively slow, and fires are infrequent. The differences between forests must, therefore, be taken into consideration when determining how they should be managed to store carbon.[38][39]

Old-growth forests have the potential to impact climate change, but climate change is also impacting old-growth forests. As the effects of global warming grow more substantial, the ability of old-growth forests to sequester carbon is affected. Climate change showed an impact on the mortality of some dominant tree species, as observed in the Korean pine.[40] Climate change also showed an effect on the composition of species when forests were surveyed over a 10- and 20-year period, which may disrupt the overall productivity of the forest.[41]

Logging edit

 
Old-growth red cedar stump near Port Renfrew, British Columbia

According to the World Resources Institute, as of January 2009, only 21% of the original old-growth forests that once existed on Earth are remaining.[42] An estimated one-half of Western Europe's forests were cleared before the Middle Ages,[43] and 90% of the old-growth forests that existed in the contiguous United States in the 1600s have been cleared.[44]

The large trees in old-growth forests are economically valuable, and have been subject to aggressive logging throughout the world. This has led to many conflicts between logging companies and environmental groups. From certain forestry perspectives, fully maintaining an old-growth forest is seen as extremely economically unproductive, as timber can only be collected from falling trees, and also potentially damaging to nearby managed groves by creating environments conducive to root rot. It may be more productive to cut the old growth down and replace the forest with a younger one.[citation needed]

The island of Tasmania, just off the southeast coast of Australia, has the largest amount of temperate old-growth rainforest reserves in Australia with around 1,239,000 hectares in total.[45] While the local Regional Forest Agreement (RFA) was originally designed to protect much of this natural wealth, many of the RFA old-growth forests protected in Tasmania consist of trees of little use to the timber industry. RFA old-growth and high conservation value forests that contain species highly desirable to the forestry industry have been poorly preserved. Only 22% of Tasmania's original tall-eucalypt forests managed by Forestry Tasmania have been reserved. Ten thousand hectares of tall-eucalypt RFA old-growth forest have been lost since 1996, predominantly as a result of industrial logging operations. In 2006, about 61,000 hectares of tall-eucalypt RFA old-growth forests remained unprotected.[46] Recent logging attempts in the Upper Florentine Valley have sparked a series of protests and media attention over the arrests that have taken place in this area. Additionally, Gunns Limited, the primary forestry contractor in Tasmania, has been under recent criticism by political and environmental groups over its practice of woodchipping timber harvested from old-growth forests.[citation needed]

Management edit

 
Old-growth forest in the Opal Creek Wilderness, a wilderness area located in the Willamette National Forest in the U.S. state of Oregon, on the border of Mount Hood National Forest. It has the largest uncut watershed in Oregon.[47]

Increased understanding of forest dynamics in the late 20th century led the scientific community to identify a need to inventory, understand, manage, and conserve representative examples of old-growth forests with their associated characteristics and values.[48] Literature around old growth and its management is inconclusive about the best way to characterize the true essence of an old-growth stand.[citation needed]

A better understanding of natural systems has resulted in new ideas about forest management, such as managed natural disturbances should be designed to achieve the landscape patterns and habitat conditions that are normally maintained in nature.[49] This coarse filter approach to biodiversity conservation recognizes ecological processes and provides for a dynamic distribution of old growth across the landscape.[48] And all seral stages—young, medium and, old—support forest biodiversity. Plants and animals rely on different forest ecosystem stages to meet their habitat needs.[50]

In Australia, the Regional Forest Agreement (RFA) attempted to prevent the clearfelling of defined "old-growth forests". This led to struggles over what constitutes "old growth". For example, in Western Australia, the timber industry tried to limit the area of old growth in the karri forests of the Southern Forests Region; this led to the creation of the Western Australian Forests Alliance, the splitting of the Liberal Government of Western Australia and the election of the Gallop Labor Government. Old-growth forests in this region have now been placed inside national parks. A small proportion of old-growth forest also exists in South-West Australia, and is protected by federal laws from logging, which has not occurred there for more than 20 years.[citation needed]

In British Columbia, Canada, old-growth forests must be maintained in each of the province's ecological units to meet biodiversity needs.[8]

Locations of remaining tracts edit

In 2006, Greenpeace identified that the world's remaining intact forest landscapes are distributed among the continents as follows:[51]

  • 35% in South America: The Amazon rainforest is mainly located in Brazil, which clears a larger area of forest annually than any other country in the world.[52]
  • 28% in North America, which harvests 10,000 km2 of ancient forests every year. Many of the fragmented forests of southern Canada and the United States lack adequate animal travel corridors and functioning ecosystems for large mammals.[52] Most of the remaining old-growth forests in the contiguous United States and Alaska are on public land.[44][dead link]
  • 19% in northern Asia, home to the largest boreal forest in the world[53]
  • 8% in Africa, which has lost most of its intact forest landscapes in the last 30 years. The timber industry and local governments are responsible for destroying huge areas of intact forest landscapes and continue to be the single largest threat to these areas.
  • 7% in South Asia Pacific, where the Paradise Forests are being destroyed faster than any other forest on Earth. Much of the large, intact forest landscapes have already been cut down, 72% in Indonesia, and 60% in Papua New Guinea.[52]
  • Less than 3% in Europe, where more than 150 km2 of intact forest landscapes are cleared every year and the last areas of the region's intact forest landscapes in European Russia are shrinking rapidly.[52] In the United Kingdom, they are known as ancient woodlands.

See also edit

Notes edit

  1. ^ Sometimes considered synonymous with the terms primary forest, virgin forest, late seral forest, primeval forest, first-growth forest, and mature forest.

References edit

  1. ^ White, David; Lloyd, Thomas (1994). "Defining Old Growth: Implications For Management" (PDF). Paper Presented at the Eighth Biennial Southern Silvicultural Research Conference, Auburn, al, Nov. L-3, 1994. Eighth Biennial Southern Silvicultural Research Conference. Retrieved 23 November 2009.
  2. ^ The State of the World's Forests 2020. In brief – Forests, biodiversity and people. Rome: FAO. 2020. p. 9. doi:10.4060/ca8985en. ISBN 978-92-5-132707-4. S2CID 241416114.
  3. ^ Global Forest Resources Assessment 2020 – Key findings. Rome: FAO. 2020. doi:10.4060/ca8753en. ISBN 978-92-5-132581-0. S2CID 130116768.
  4. ^ a b c d e f Maloof, Joan (16 November 2016). Nature's Temples: The Complex World of Old-Growth Forests. Timber Press. ISBN 978-1-60469-728-5.
  5. ^ Wirth, Christian; Gleixner, Gerd; Heimann, Martin (7 July 2009). Old-Growth Forests: Function, Fate and Value. Springer Science & Business Media. ISBN 978-3-540-92706-8.
  6. ^ a b McGarvey, Jennifer; Thompson, Jonathan R.; Epstein, Howard E.; Shugart, Herman H. (1 February 2015). "Carbon storage in old-growth forests of the Mid-Atlantic: toward better understanding the eastern forest carbon sink". Ecology. 96 (2): 311–317. doi:10.1890/14-1154.1. ISSN 1939-9170. PMID 26240851.
  7. ^ a b (PDF). Archived from the original (PDF) on 4 August 2009. Retrieved 25 April 2011.
  8. ^ a b (PDF). Archived from the original (PDF) on 8 April 2020. Retrieved 25 April 2011.
  9. ^ BC Ministry of Forests 2003 Old Growth Forests
  10. ^ Williams, Jann; Woinarski, John (13 November 1997). Eucalypt Ecology. Cambridge University Press. ISBN 9780521497404.
  11. ^ (PDF). Archived from the original (PDF) on 3 October 2011. Retrieved 25 April 2011.
  12. ^ a b "Ministry of Natural Resources and Forestry" (PDF). Ontario.ca.
  13. ^ Protect the World’s Forests Rainforest Action Network
  14. ^ The world’s remaining great forests. The Guardian 2007
  15. ^ Stamets, Paul (2005). Mycelium Running. Ten Speed Press. pp. 35. ISBN 978-1-58008-579-3.
  16. ^ Provincial Non-Spatial Old Growth Order. 2004. Integrated Land Management Bureau, British Columbia, Canada
  17. ^ Forest Stand Dynamics. 1996. Oliver C.;Larson B.
  18. ^ ""Old growth in the boreal forest: A dynamic perspective at the stand and landscape level" by Daniel Kneeshaw and Sylvie Gauthier 2003". Archived from the original on 1 July 2012. Retrieved 25 April 2011.
  19. ^ Frequently Asked Questions nps.gov. Retrieved 11 February 2009.
  20. ^ Stephanie Wood. "B.C. old-growth data 'misleading' public on remaining ancient forest: independent report, June 4, 2020, The Narwhal".
  21. ^ "What is old-growth forest?". 24 February 2015.
  22. ^ (PDF). Archived from the original (PDF) on 3 October 2011. Retrieved 25 April 2011.
  23. ^ (PDF). Archived from the original (PDF) on 17 June 2011. Retrieved 25 April 2011.
  24. ^ "Old-growth Forests in Canada – A Science Perspective". fao.org.
  25. ^ "Page moved - 10drugs.htm". mongabay.com.
  26. ^ The Rainforest as a Source For New Pharmaceuticals August 2008 from Network Science website
  27. ^ . grida.no. Archived from the original on 29 September 2007. Retrieved 21 April 2007.
  28. ^ Luyssaert, S; Schulze, ED (2008). "Old-growth forests as global carbon sinks" (PDF). Nature. 455 (7210): 213–5. Bibcode:2008Natur.455..213L. doi:10.1038/nature07276. PMID 18784722. S2CID 4424430.
  29. ^ (PDF). Archived from the original (PDF) on 3 October 2011. Retrieved 25 April 2011.
  30. ^ Brothers, Timothy S.; Spingarn, Arthur (1992). "Forest Fragmentation and Alien Plant Invasion of Central Indiana Old-Growth Forests". Conservation Biology. 6 (1): 91–100. doi:10.1046/j.1523-1739.1992.610091.x. ISSN 1523-1739.
  31. ^ Old-Growth Forests Can Actually Contribute to Global Warming, Wired, 19 May 2008
  32. ^ [Ter-Mikaelian, M. T., S. J. Colombo, et al. 2008. "Fact and fantasy about forest carbon." Forestry Chronicle 84(2): 166–171]
  33. ^ Keith, Heather; Mackey, Brendan G.; Lindenmayer, David B. (14 July 2009). "Re-evaluation of forest biomass carbon stocks and lessons from the world's most carbon-dense forests". Proceedings of the National Academy of Sciences. 106 (28): 11635–11640. Bibcode:2009PNAS..10611635K. doi:10.1073/pnas.0901970106. ISSN 0027-8424. PMC 2701447. PMID 19553199.
  34. ^ Ryan, Michael G.; Harmon, Mark E.; Birdsey, Richard A.; Giardina, Christian P.; Heath, Linda S.; Houghton, Richard A.; Jackson, Robert B.; McKinley, Duncan C.; Morrison, James F.; Murray, Brian C.; Pataki, Diane E.; Skog, Kenneth E. (2010). . Fs.fed.us: 1–16. Archived from the original on 30 April 2017. Retrieved 25 April 2011.
  35. ^ Eartha Jane Melzer (26 January 2010). . The Michigan Messenger. Archived from the original on 5 February 2010.
  36. ^ Zhang, J.; Smith, K. R. (2007). "Household Air Pollution from Coal and Biomass Fuels in China: Measurements, Health Impacts, and Interventions". Environmental Health Perspectives. 115 (6): 848–855. doi:10.1289/ehp.9479. PMC 1892127. PMID 17589590.
  37. ^ "Announcement". Archives of Virology. 130 (1–2): 225. 1993. doi:10.1007/BF01319012.
  38. ^ (PDF). Archived from the original (PDF) on 11 May 2012. Retrieved 25 April 2011.
  39. ^ . grida.no. Archived from the original on 31 August 2021. Retrieved 1 March 2012.
  40. ^ Dai, Limin; Jia, Juan; Yu, Dapao; Lewis, Bernard J.; Zhou, Li; Zhou, Wangming; Zhao, Wei; Jiang, Linhai (15 July 2013). "Effects of climate change on biomass carbon sequestration in old-growth forest ecosystems on Changbai Mountain in Northeast China". Forest Ecology and Management. Shaping Forest Management to Climate Change. 300: 106–116. doi:10.1016/j.foreco.2012.06.046.
  41. ^ van der Sande, Masha T.; Arets, Eric J. M. M.; Peña-Claros, Marielos; de Avila, Angela Luciana; Roopsind, Anand; Mazzei, Lucas; Ascarrunz, Nataly; Finegan, Bryan; Alarcón, Alfredo (1 May 2016). "Old-growth Neotropical forests are shifting in species and trait composition". Ecological Monographs. 86 (2): 228–243. doi:10.1890/15-1815.1. ISSN 1557-7015.
  42. ^ World Resources Institute, State of the World's Forests, 8 January 2009. Retrieved 24 May 2013
  43. ^ Food and Agriculture Organization, State of the world's forests, 2012, p.11. Retrieved 24 May 2013
  44. ^ a b David Allan, Global deforestation 15 June 2011 at the Wayback Machine, Global change program, University of Michigan, 1 April 2010. Retrieved 24 May 2013
  45. ^ . Archived from the original on 24 August 2011. Retrieved 17 October 2011.
  46. ^ Majewski, Ula. . foe.org.au. Archived from the original on 9 April 2011.
  47. ^ "Opal Creek Wilderness". The Cranberry House. Retrieved 20 August 2007.
  48. ^ a b (PDF). Archived from the original (PDF) on 3 October 2011. Retrieved 25 April 2011.
  49. ^ (DeLong 1998; Wong and Iverson 2004).
  50. ^ BC Ministry of Forests Research Program Seral Stages across forested landscapes 1998
  51. ^ "Intact Forest Landscapes". intactforests.org.
  52. ^ a b c d "Intact Forest Landscapes". Greenpeace International. Archived from the original on 18 May 2020.
  53. ^ "BOREALFOREST.ORG – Boreal Forests of the World – Introduction". borealforest.org. 30 August 2022.

Sources edit

  This article incorporates text from a free content work. Licensed under CC BY-SA 3.0 (license statement/permission). Text taken from Global Forest Resources Assessment 2020 Key findings​, FAO, FAO.   This article incorporates text from a free content work. Licensed under CC BY-SA 3.0 (license statement/permission). Text taken from The State of the World's Forests 2020. In brief – Forests, biodiversity and people​, FAO & UNEP, FAO & UNEP.

Further reading edit

External links edit

  • Our disappearing forests 24 September 2008 at the Wayback Machine
  • Rainforest Action Network
  • Ancient Forest Exploration & Research
  • Natural Resources Canada 2003
  • Old Growth Forest Definitions for Ontario
  • Submissions to XII World Forest Congress 2003
  • Minnesota Department of Natural Resources 17 May 2019 at the Wayback Machine
  • Archangel Ancient Tree Archive | Old Growth Trees

growth, forest, growth, redirects, here, dead, meadow, album, growth, album, virgin, forest, redirects, here, 1985, movie, virgin, forest, 2022, movie, virgin, forest, 2022, film, growth, forest, forest, that, developed, over, long, period, time, without, dist. Old growth redirects here For the Dead Meadow album see Old Growth album Virgin forest redirects here For the 1985 movie see Virgin Forest For the 2022 movie see Virgin Forest 2022 film An old growth forest a is a forest that has developed over a long period of time without disturbance Due to this old growth forests exhibit unique ecological features 1 The Food and Agriculture Organization of the United Nations defines primary forests as naturally regenerated forests of native tree species where there are no clearly visible indications of human activity and the ecological processes are not significantly disturbed Barely one third 34 percent of the world s forests are primary forests 2 Old growth features include diverse tree related structures that provide diverse wildlife habitats that increases the biodiversity of the forested ecosystem Virgin or first growth forests are old growth forests that have never been logged The concept of diverse tree structure includes multi layered canopies and canopy gaps greatly varying tree heights and diameters and diverse tree species and classes and sizes of woody debris Old growth European beech forest in Biogradska Gora National Park MontenegroCool temperate rainforest in Tasmania AustraliaFirst growth or virgin forest near Mount RainierAs of 2020 update the world has 1 11 billion ha of primary forest remaining Combined three countries Brazil Canada and Russia host more than half 61 percent of the world s primary forest The area of primary forest has decreased by 81 million ha since 1990 but the rate of loss more than halved in 2010 2020 compared with the previous decade 3 Old growth forests are valuable for economic reasons and for the ecosystem services they provide 4 5 This can be a point of contention when some in the logging industry desire to harvest valuable timber from the forests destroying the forests in the process to generate short term profits while environmentalists seek to preserve the forests in their pristine state for benefits such as water purification flood control weather stability maintenance of biodiversity and nutrient cycling Moreover old growth forests are more efficient at sequestering carbon than newly planted forests and fast growing timber plantations thus preserving the forests is important to climate change mitigation 6 7 Contents 1 Characteristics 1 1 Biodiversity 1 2 Mixed age 1 3 Canopy openings 1 4 Topography 1 5 Standing snags 1 6 Decaying ground layer 1 7 Soil 2 Definitions 2 1 Ecological definitions 2 1 1 Stand age definition 2 1 2 Forest dynamics definition 2 2 Social and cultural definitions 2 3 Economic definitions 2 4 Other definitions 3 Importance 4 Ecosystem services 5 Climatic impacts 6 Logging 7 Management 8 Locations of remaining tracts 9 See also 10 Notes 11 References 12 Sources 13 Further reading 14 External linksCharacteristics edit nbsp Antarctic beech old growth in Lamington National Park Queensland AustraliaOld growth forests tend to have large trees and standing dead trees multilayered canopies with gaps that result from the deaths of individual trees and coarse woody debris on the forest floor 8 A forest regenerated after a severe disturbance such as wildfire insect infestation or harvesting is often called second growth or regeneration until enough time passes for the effects of the disturbance to be no longer evident Depending on the forest this may take from a century to several millennia Hardwood forests of the eastern United States can develop old growth characteristics in 150 500 years In British Columbia Canada old growth is defined as 120 to 140 years of age in the interior of the province where fire is a frequent and natural occurrence In British Columbia s coastal rainforests old growth is defined as trees more than 250 years with some trees reaching more than 1 000 years of age 9 In Australia eucalypt trees rarely exceed 350 years of age due to frequent fire disturbance 10 Forest types have very different development patterns natural disturbances and appearances A Douglas fir stand may grow for centuries without disturbance while an old growth ponderosa pine forest requires frequent surface fires to reduce the shade tolerant species and regenerate the canopy species 11 In the boreal forest of Canada catastrophic disturbances like wildfires minimize opportunities for major accumulations of dead and downed woody material and other structural legacies associated with old growth conditions 12 Typical characteristics of old growth forest include the presence of older trees minimal signs of human disturbance mixed age stands presence of canopy openings due to tree falls pit and mound topography down wood in various stages of decay standing snags dead trees multilayered canopies intact soils a healthy fungal ecosystem and presence of indicator species citation needed Biodiversity edit nbsp The northern spotted owl primarily inhabits old growth forests in the northern part of its range Canada to southern Oregon and landscapes with a mix of old and younger forest types in the southern part of its range the Klamath region and California Old growth forests are often biologically diverse and home to many rare species threatened species and endangered species of plants and animals such as the northern spotted owl marbled murrelet and fisher making them ecologically significant Levels of biodiversity may be higher or lower in old growth forests compared to that in second growth forests depending on specific circumstances environmental variables and geographic variables Logging in old growth forests is a contentious issue in many parts of the world Excessive logging reduces biodiversity affecting not only the old growth forest itself but also indigenous species that rely upon old growth forest habitat 13 14 Mixed age edit This section does not cite any sources Please help improve this section by adding citations to reliable sources Unsourced material may be challenged and removed December 2022 Learn how and when to remove this template message Some forests in the old growth stage have a mix of tree ages due to a distinct regeneration pattern for this stage New trees regenerate at different times from each other because each of them has a different spatial location relative to the main canopy hence each one receives a different amount of light The mixed age of the forest is an important criterion in ensuring that the forest is a relatively stable ecosystem in the long term A climax stand that is uniformly aged becomes senescent and degrades within a relatively short time to result in a new cycle of forest succession Thus uniformly aged stands are less stable ecosystems Boreal forests are more uniformly aged as they are normally subject to frequent stand replacing wildfires Canopy openings edit Forest canopy gaps are essential in creating and maintaining mixed age stands Also some herbaceous plants only become established in canopy openings but persist beneath an understory Openings are a result of tree death due to small impact disturbances such as wind low intensity fires and tree diseases Old growth forests are unique usually having multiple horizontal layers of vegetation representing a variety of tree species age classes and sizes as well as pit and mound soil shape with well established fungal nets 15 Because old growth forest is structurally diverse it provides higher diversity habitat than forests in other stages Thus sometimes higher biological diversity can be sustained in old growth forests or at least a biodiversity that is different from other forest stages nbsp Virgin forest about 2500 m above sea level in Shennongjia Forestry District Hubei ChinaTopography edit The characteristic topography of much old growth forest consists of pits and mounds Mounds are caused by decaying fallen trees and pits tree throws by the roots pulled out of the ground when trees fall due to natural causes including being pushed over by animals Pits expose humus poor mineral rich soil and often collect moisture and fallen leaves forming a thick organic layer that is able to nurture certain types of organisms Mounds provide a place free of leaf inundation and saturation where other types of organisms thrive 4 Standing snags edit Standing snags provide food sources and habitat for many types of organisms In particular many species of dead wood predators such as woodpeckers must have standing snags available for feeding In North America the spotted owl is well known for needing standing snags for nesting habitat 4 Decaying ground layer edit nbsp Downed wood replenishes topsoil as it decays nbsp Fungus Climacocystis borealis on a tree stump in the Bialowieza Forest one of the last largely intact primeval forests in Central EuropeFallen timber or coarse woody debris contributes carbon rich organic matter directly to the soil providing a substrate for mosses fungi and seedlings and creating microhabitats by creating relief on the forest floor In some ecosystems such as the temperate rain forest of the North American Pacific coast fallen timber may become nurse logs providing a substrate for seedling trees 4 Soil edit Intact soils harbor many life forms that rely on them Intact soils generally have very well defined horizons or soil profiles Different organisms may need certain well defined soil horizons to live while many trees need well structured soils free of disturbance to thrive Some herbaceous plants in northern hardwood forests must have thick duff layers which are part of the soil profile Fungal ecosystems are essential for efficient in situ recycling of nutrients back into the entire ecosystem 4 Definitions editEcological definitions edit Stand age definition edit Stand age can also be used to categorize a forest as old growth 16 For any given geographical area the average time since disturbance until a forest reaches the old growth stage can be determined This method is useful because it allows quick and objective determination of forest stage However this definition does not provide an explanation of forest function It just gives a useful number to measure So some forests may be excluded from being categorized as old growth even if they have old growth attributes just because they are too young Also older forests can lack some old growth attributes and be categorized as old growth just because they are so old The idea of using age is also problematic because human activities can influence the forest in varied ways For example after the logging of 30 of the trees less time is needed for old growth to come back than after removal of 80 of the trees Although depending on the species logged the forest that comes back after a 30 harvest may consist of proportionately fewer hardwood trees than a forest logged at 80 in which the light competition by less important tree species does not inhibit the regrowth of vital hardwoods Forest dynamics definition edit From a forest dynamics perspective old growth forest is in a stage that follows understory reinitiation stage 17 A review of the stages helps to understand the concept Stand replacing Disturbance hits the forest and kills most of the living trees Stand initiation A population of new trees becomes established Stem exclusion Trees grow higher and enlarge their canopy thus competing for the light with neighbors light competition mortality kills slow growing trees and reduces forest density which allows surviving trees to increase in size Eventually the canopies of neighboring trees touch each other and drastically lower the amount of light that reaches lower layers Due to that the understory dies and only very shade tolerant species survive Understory reinitiation Trees die from low level mortality such as windthrow and diseases Individual canopy gaps start to appear and more light can reach the forest floor Hence shade tolerant species can establish in the understory Old growth Main canopy trees become older and more of them die creating even more gaps Since the gaps appear at different times the understory trees are at different growth stages Furthermore the amount of light that reaches each understory tree depends on its position relative to the gap Thus each understory tree grows at a different rate The differences in establishment timing and in growth rate create a population of understory trees that is variable in size Eventually some understory trees grow to become as tall as the main canopy trees thereby filling the gap This perpetuation process is typical for the old growth stage This however does not mean that the forest will be old growth forever Generally three futures for old growth stage forest are possible 1 The forest will be hit by a disturbance and most of the trees will die 2 Unfavorable conditions for new trees to regenerate will occur In this case the old trees will die and smaller plants will create woodland and 3 The regenerating understory trees are different species from the main canopy trees In this case the forest will switch back to stem exclusion stage but with shade tolerant tree species 4 The forest in an old growth stage can be stable for centuries but the length of this stage depends on the forest s tree composition and the climate of the area For example frequent natural fires do not allow boreal forests to be as old as coastal forests of western North America Of importance is that while the stand switches from one tree community to another the stand will not necessarily go through old growth stage between those stages Some tree species have a relatively open canopy That allows more shade tolerant tree species to establish below even before the understory reinitiation stage The shade tolerant trees eventually outcompete the main canopy trees in stem exclusion stage Therefore the dominant tree species will change but the forest will still be in stem exclusion stage until the shade tolerant species reach old growth stage Tree species succession may change tree species composition once the old growth stage has been achieved For example an old boreal forest may contain some large aspen trees which may die and be replaced by smaller balsam fir or black spruce Consequently the forest will switch back to understory reinitiation stage 18 Using the stand dynamics definition old growth can be easily evaluated using structural attributes However in some forest ecosystems this can lead to decisions regarding the preservation of unique stands or attributes that will disappear over the next few decades because of natural succession processes Consequently using stand dynamics to define old growth forests is more accurate in forests where the species that constitute old growth have long lifespans and succession is slow 4 Social and cultural definitions edit nbsp Redwood tree in northern California redwood forest According to the National Park Service 96 percent of the original old growth coast redwoods have been logged 19 Common cultural definitions and common denominators regarding what comprises old growth forest and the variables that define constitute and embody old growth forests include The forest habitat possesses relatively mature old trees The tree species present have long continuity on the same site The forest itself is a remnant natural area that has not been subjected to significant disturbance by mankind altering the appearance of the landscape and its ecosystems has not been subjected to logging or other types of development such as road networks or housing and has inherently progressed per natural tendencies Additionally in mountainous temperate landscapes such as Western North America and specifically in areas of high quality soil and a moist relatively mild climate some old growth trees have attained notable height and girth DBH diameter at breast height accompanied by notable biodiversity in terms of the species supported Therefore for most people the physical size of the trees is the most recognized hallmark of old growth forests even though the ecologically productive areas that support such large trees often comprise only a very small portion of the total area that has been mapped as old growth forest 20 In high altitude harsh climates trees grow very slowly and thus remain at a small size Such trees also qualify as old growth in terms of how they are mapped but are rarely recognized by the general public as such The debate over old growth definitions has been inextricably linked with a complex range of social perceptions about wilderness preservation biodiversity aesthetics and spirituality as well as economic or industrial values 12 21 Economic definitions edit In logging terms old growth stands are past the economic optimum for harvesting usually between 80 and 150 years depending on the species Old growth forests were often given harvesting priority clarification needed because they had the most commercially valuable timber they were considered to be at greater risk of deterioration through root rot or insect infestation and they occupied land that could be used for more productive second growth stands 22 In some regions old growth is not the most commercially viable timber in British Columbia Canada harvesting in the coastal region is moving to younger second growth stands 23 Other definitions edit A 2001 scientific symposium in Canada found that defining old growth in a scientifically meaningful yet policy relevant manner presents some basic difficulties especially if a simple unambiguous and rigorous scientific definition is sought Symposium participants identified some attributes of late successional temperate zone old growth forest types that could be considered in developing an index of old growthness and for defining old growth forests 24 Structural features nbsp Avatar Grove near Port Renfrew British Columbia Giant Douglas firs left and red cedars right fill the grove Uneven or multi aged stand structure or several identifiable age cohorts Average age of dominant species approaching half the maximum longevity for species about 150 years for most shade tolerant trees Some old trees at close to their maximum longevity ages of 300 years Presence of standing dead and dying trees in various stages of decay Fallen coarse woody debris Natural regeneration of dominant tree species within canopy gaps or on decaying logsCompositional features Long lived shade tolerant tree species associations e g sugar maple American beech yellow birch red spruce eastern hemlock white pine Process features Characterized by small scale disturbances creating gaps in the forest canopy A long natural rotation for catastrophic or stand replacing disturbance e g a period greater than the maximum longevity of the dominant tree species Minimal evidence of human disturbance Final stages of stand development before a relatively steady state is reachedImportance edit nbsp Eucalyptus regnans forest in Tasmania AustraliaOld growth forests often contain rich communities of plants and animals within the habitat due to the long period of forest stability These varied and sometimes rare species may depend on the unique environmental conditions created by these forests Old growth forests serve as a reservoir for species which cannot thrive or easily regenerate in younger forests so they can be used as a baseline for research Plant species that are native to old growth forests may someday prove to be invaluable towards curing various human ailments as has been realized in numerous plants in tropical rainforests 25 26 Old growth forests also store large amounts of carbon above and below the ground either as humus or in wet soils as peat They collectively represent a very significant store of carbon Destruction of these forests releases this carbon as greenhouse gases and may increase the risk of global climate change 27 Although old growth forests serve as a global carbon dioxide sink they are not protected by international treaties because it is generally thought that aging forests cease to accumulate carbon However in forests between 15 and 800 years of age net ecosystem productivity the net carbon balance of the forest including soils is usually positive old growth forests accumulate carbon for centuries and contain large quantities of it 28 Ecosystem services editOld growth forests provide ecosystem services that may be far more important to society than their use as a source of raw materials These services include making breathable air making pure water carbon storage regeneration of nutrients maintenance of soils pest control by insectivorous bats and insects micro and macro climate control and the storage of a wide variety of genes 29 30 Climatic impacts editThe effects of old growth forests in relation to global warming have been addressed in various studies and journals The Intergovernmental Panel on Climate Change said in its 2007 report In the long term a sustainable forest management strategy aimed at maintaining or increasing forest carbon stocks while producing an annual sustained yield of timber fibre or energy from the forest will generate the largest sustained mitigation benefit 7 Old growth forests are often perceived to be in equilibrium or in a state of decay 31 However evidence from analysis of carbon stored above ground and in the soil has shown old growth forests are more productive at storing carbon than younger forests 6 Forest harvesting has little or no effect on the amount of carbon stored in the soil 32 but other research suggests older forests that have trees of many ages multiple layers and little disturbance have the highest capacities for carbon storage 33 As trees grow they remove carbon from the atmosphere and protecting these pools of carbon prevents emissions into the atmosphere Proponents of harvesting the forest argue the carbon stored in wood is available for use as biomass energy displacing fossil fuel use 34 although using biomass as a fuel produces air pollution in the form of carbon monoxide nitrogen oxides volatile organic compounds particulates and other pollutants in some cases at levels above those from traditional fuel sources such as coal or natural gas 35 36 37 Each forest has a different potential to store carbon For example this potential is particularly high in the Pacific Northwest where forests are relatively productive trees live a long time decomposition is relatively slow and fires are infrequent The differences between forests must therefore be taken into consideration when determining how they should be managed to store carbon 38 39 Old growth forests have the potential to impact climate change but climate change is also impacting old growth forests As the effects of global warming grow more substantial the ability of old growth forests to sequester carbon is affected Climate change showed an impact on the mortality of some dominant tree species as observed in the Korean pine 40 Climate change also showed an effect on the composition of species when forests were surveyed over a 10 and 20 year period which may disrupt the overall productivity of the forest 41 Logging editFurther information Deforestation See also Deforestation Historical causes nbsp Old growth red cedar stump near Port Renfrew British ColumbiaAccording to the World Resources Institute as of January 2009 only 21 of the original old growth forests that once existed on Earth are remaining 42 An estimated one half of Western Europe s forests were cleared before the Middle Ages 43 and 90 of the old growth forests that existed in the contiguous United States in the 1600s have been cleared 44 The large trees in old growth forests are economically valuable and have been subject to aggressive logging throughout the world This has led to many conflicts between logging companies and environmental groups From certain forestry perspectives fully maintaining an old growth forest is seen as extremely economically unproductive as timber can only be collected from falling trees and also potentially damaging to nearby managed groves by creating environments conducive to root rot It may be more productive to cut the old growth down and replace the forest with a younger one citation needed The island of Tasmania just off the southeast coast of Australia has the largest amount of temperate old growth rainforest reserves in Australia with around 1 239 000 hectares in total 45 While the local Regional Forest Agreement RFA was originally designed to protect much of this natural wealth many of the RFA old growth forests protected in Tasmania consist of trees of little use to the timber industry RFA old growth and high conservation value forests that contain species highly desirable to the forestry industry have been poorly preserved Only 22 of Tasmania s original tall eucalypt forests managed by Forestry Tasmania have been reserved Ten thousand hectares of tall eucalypt RFA old growth forest have been lost since 1996 predominantly as a result of industrial logging operations In 2006 about 61 000 hectares of tall eucalypt RFA old growth forests remained unprotected 46 Recent logging attempts in the Upper Florentine Valley have sparked a series of protests and media attention over the arrests that have taken place in this area Additionally Gunns Limited the primary forestry contractor in Tasmania has been under recent criticism by political and environmental groups over its practice of woodchipping timber harvested from old growth forests citation needed Management edit nbsp Old growth forest in the Opal Creek Wilderness a wilderness area located in the Willamette National Forest in the U S state of Oregon on the border of Mount Hood National Forest It has the largest uncut watershed in Oregon 47 Increased understanding of forest dynamics in the late 20th century led the scientific community to identify a need to inventory understand manage and conserve representative examples of old growth forests with their associated characteristics and values 48 Literature around old growth and its management is inconclusive about the best way to characterize the true essence of an old growth stand citation needed A better understanding of natural systems has resulted in new ideas about forest management such as managed natural disturbances should be designed to achieve the landscape patterns and habitat conditions that are normally maintained in nature 49 This coarse filter approach to biodiversity conservation recognizes ecological processes and provides for a dynamic distribution of old growth across the landscape 48 And all seral stages young medium and old support forest biodiversity Plants and animals rely on different forest ecosystem stages to meet their habitat needs 50 In Australia the Regional Forest Agreement RFA attempted to prevent the clearfelling of defined old growth forests This led to struggles over what constitutes old growth For example in Western Australia the timber industry tried to limit the area of old growth in the karri forests of the Southern Forests Region this led to the creation of the Western Australian Forests Alliance the splitting of the Liberal Government of Western Australia and the election of the Gallop Labor Government Old growth forests in this region have now been placed inside national parks A small proportion of old growth forest also exists in South West Australia and is protected by federal laws from logging which has not occurred there for more than 20 years citation needed In British Columbia Canada old growth forests must be maintained in each of the province s ecological units to meet biodiversity needs 8 Locations of remaining tracts editMain article List of old growth forests In 2006 Greenpeace identified that the world s remaining intact forest landscapes are distributed among the continents as follows 51 35 in South America The Amazon rainforest is mainly located in Brazil which clears a larger area of forest annually than any other country in the world 52 28 in North America which harvests 10 000 km2 of ancient forests every year Many of the fragmented forests of southern Canada and the United States lack adequate animal travel corridors and functioning ecosystems for large mammals 52 Most of the remaining old growth forests in the contiguous United States and Alaska are on public land 44 dead link 19 in northern Asia home to the largest boreal forest in the world 53 8 in Africa which has lost most of its intact forest landscapes in the last 30 years The timber industry and local governments are responsible for destroying huge areas of intact forest landscapes and continue to be the single largest threat to these areas 7 in South Asia Pacific where the Paradise Forests are being destroyed faster than any other forest on Earth Much of the large intact forest landscapes have already been cut down 72 in Indonesia and 60 in Papua New Guinea 52 Less than 3 in Europe where more than 150 km2 of intact forest landscapes are cleared every year and the last areas of the region s intact forest landscapes in European Russia are shrinking rapidly 52 In the United Kingdom they are known as ancient woodlands See also editClearcutting Forestry logging practice in which most or all trees in an area are uniformly cut down Cloud forest Type of rainforest Conservation reliant species Earth science Fields of natural science related to Earth Forest ecology Study of interactions between the biota and environment in forests Forest migration movement of large seed plant dominated communities in geographical space over timePages displaying wikidata descriptions as a fallback Forestry Commission UK non ministerial government department responsible for forests Habitat conservation Management practice for protecting types of environments History of the forest in Central Europe Illegal logging Harvest transportation purchase or sale of timber in violation of laws Jungle An impassable dense forest typically tropical Kelp forest Underwater areas with a high density of kelp List of countries by forest area List of superlative trees Natural capital World s stock of natural resources Natural environment Living and non living things on Earth Natural landscape Original landscape formed by nature Natural resource Resources that exist without actions of humankind Old Growth Forest Network American non profit organization Plantation Agricultural estate growing cash crops forestry REDD plus Climate change mitigation policyPages displaying short descriptions of redirect targets Sky island Geographic or environmental feature Subalpine Ecosystems found in mountainsPages displaying short descriptions of redirect targets forest Sustainable development Mode of human development Taiga Biome characterized by coniferous forests Temperate broadleaf and mixed forest BiomePages displaying short descriptions of redirect targets Pages displaying short descriptions with no spaces Temperate coniferous forest Forests found in areas with warm summers and cool winters Tropical and subtropical coniferous forests Tropical forest habitat type Tropical and subtropical moist broadleaf forests Habitat type defined by the World Wide Fund for Nature Woodland management Branch of forestryPages displaying short descriptions of redirect targetsNotes edit Sometimes considered synonymous with the terms primary forest virgin forest late seral forest primeval forest first growth forest and mature forest References edit White David Lloyd Thomas 1994 Defining Old Growth Implications For Management PDF Paper Presented at the Eighth Biennial Southern Silvicultural Research Conference Auburn al Nov L 3 1994 Eighth Biennial Southern Silvicultural Research Conference Retrieved 23 November 2009 The State of the World s Forests 2020 In brief Forests biodiversity and people Rome FAO 2020 p 9 doi 10 4060 ca8985en ISBN 978 92 5 132707 4 S2CID 241416114 Global Forest Resources Assessment 2020 Key findings Rome FAO 2020 doi 10 4060 ca8753en ISBN 978 92 5 132581 0 S2CID 130116768 a b c d e f Maloof Joan 16 November 2016 Nature s Temples The Complex World of Old Growth Forests Timber Press ISBN 978 1 60469 728 5 Wirth Christian Gleixner Gerd Heimann Martin 7 July 2009 Old Growth Forests Function Fate and Value Springer Science amp Business Media ISBN 978 3 540 92706 8 a b McGarvey Jennifer Thompson Jonathan R Epstein Howard E Shugart Herman H 1 February 2015 Carbon storage in old growth forests of the Mid Atlantic toward better understanding the eastern forest carbon sink Ecology 96 2 311 317 doi 10 1890 14 1154 1 ISSN 1939 9170 PMID 26240851 a b Contribution of Working Group III to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change 2007 B Metz O R Davidson P R Bosch R Dave L A Meyer eds Cambridge University Press Cambridge United Kingdom and New York NY USA PDF Archived from the original PDF on 4 August 2009 Retrieved 25 April 2011 a b Naturally wood British Columbia s Forest Diversity PDF Archived from the original PDF on 8 April 2020 Retrieved 25 April 2011 BC Ministry of Forests 2003 Old Growth Forests Williams Jann Woinarski John 13 November 1997 Eucalypt Ecology Cambridge University Press ISBN 9780521497404 Old growth definitions and management A literature review BC Journal of Ecosystems and Management PDF Archived from the original PDF on 3 October 2011 Retrieved 25 April 2011 a b Ministry of Natural Resources and Forestry PDF Ontario ca Protect the World s Forests Rainforest Action Network The world s remaining great forests The Guardian 2007 Stamets Paul 2005 Mycelium Running Ten Speed Press pp 35 ISBN 978 1 58008 579 3 Provincial Non Spatial Old Growth Order 2004 Integrated Land Management Bureau British Columbia Canada Forest Stand Dynamics 1996 Oliver C Larson B Old growth in the boreal forest A dynamic perspective at the stand and landscape level by Daniel Kneeshaw and Sylvie Gauthier 2003 Archived from the original on 1 July 2012 Retrieved 25 April 2011 Frequently Asked Questions nps gov Retrieved 11 February 2009 Stephanie Wood B C old growth data misleading public on remaining ancient forest independent report June 4 2020 The Narwhal What is old growth forest 24 February 2015 Old growth definitions and management A literature review BC Journal of Ecosystems and Management P 17 PDF Archived from the original PDF on 3 October 2011 Retrieved 25 April 2011 Coastal Action Plan page 4 PDF Archived from the original PDF on 17 June 2011 Retrieved 25 April 2011 Old growth Forests in Canada A Science Perspective fao org Page moved 10drugs htm mongabay com The Rainforest as a Source For New Pharmaceuticals August 2008 from Network Science website Climate Change 2001 The Scientific Basis grida no Archived from the original on 29 September 2007 Retrieved 21 April 2007 Luyssaert S Schulze ED 2008 Old growth forests as global carbon sinks PDF Nature 455 7210 213 5 Bibcode 2008Natur 455 213L doi 10 1038 nature07276 PMID 18784722 S2CID 4424430 Old growth definitions and management A literature review BC Journal of Ecosystems and Management P 22 PDF Archived from the original PDF on 3 October 2011 Retrieved 25 April 2011 Brothers Timothy S Spingarn Arthur 1992 Forest Fragmentation and Alien Plant Invasion of Central Indiana Old Growth Forests Conservation Biology 6 1 91 100 doi 10 1046 j 1523 1739 1992 610091 x ISSN 1523 1739 Old Growth Forests Can Actually Contribute to Global Warming Wired 19 May 2008 Ter Mikaelian M T S J Colombo et al 2008 Fact and fantasy about forest carbon Forestry Chronicle 84 2 166 171 Keith Heather Mackey Brendan G Lindenmayer David B 14 July 2009 Re evaluation of forest biomass carbon stocks and lessons from the world s most carbon dense forests Proceedings of the National Academy of Sciences 106 28 11635 11640 Bibcode 2009PNAS 10611635K doi 10 1073 pnas 0901970106 ISSN 0027 8424 PMC 2701447 PMID 19553199 Ryan Michael G Harmon Mark E Birdsey Richard A Giardina Christian P Heath Linda S Houghton Richard A Jackson Robert B McKinley Duncan C Morrison James F Murray Brian C Pataki Diane E Skog Kenneth E 2010 A synthesis of the science on forests and carbon for U S Forests Forest Service Research amp Development Fs fed us 1 16 Archived from the original on 30 April 2017 Retrieved 25 April 2011 Eartha Jane Melzer 26 January 2010 Proposed biomass plant Better than coal The Michigan Messenger Archived from the original on 5 February 2010 Zhang J Smith K R 2007 Household Air Pollution from Coal and Biomass Fuels in China Measurements Health Impacts and Interventions Environmental Health Perspectives 115 6 848 855 doi 10 1289 ehp 9479 PMC 1892127 PMID 17589590 Announcement Archives of Virology 130 1 2 225 1993 doi 10 1007 BF01319012 U S Forest Service A Synthesis of the Science on Forests and Carbon for U S Forests Page 4 PDF Archived from the original PDF on 11 May 2012 Retrieved 25 April 2011 CARBON MANAGEMENT IN NATURAL ECOSYSTEMS grida no Archived from the original on 31 August 2021 Retrieved 1 March 2012 Dai Limin Jia Juan Yu Dapao Lewis Bernard J Zhou Li Zhou Wangming Zhao Wei Jiang Linhai 15 July 2013 Effects of climate change on biomass carbon sequestration in old growth forest ecosystems on Changbai Mountain in Northeast China Forest Ecology and Management Shaping Forest Management to Climate Change 300 106 116 doi 10 1016 j foreco 2012 06 046 van der Sande Masha T Arets Eric J M M Pena Claros Marielos de Avila Angela Luciana Roopsind Anand Mazzei Lucas Ascarrunz Nataly Finegan Bryan Alarcon Alfredo 1 May 2016 Old growth Neotropical forests are shifting in species and trait composition Ecological Monographs 86 2 228 243 doi 10 1890 15 1815 1 ISSN 1557 7015 World Resources Institute State of the World s Forests 8 January 2009 Retrieved 24 May 2013 Food and Agriculture Organization State of the world s forests 2012 p 11 Retrieved 24 May 2013 a b David Allan Global deforestation Archived 15 June 2011 at the Wayback Machine Global change program University of Michigan 1 April 2010 Retrieved 24 May 2013 Forest Education Foundation Tasmania Archived from the original on 24 August 2011 Retrieved 17 October 2011 Majewski Ula Tasmania s old growth forests foe org au Archived from the original on 9 April 2011 Opal Creek Wilderness The Cranberry House Retrieved 20 August 2007 a b Old growth definitions and management A literature review BC Journal of Ecosystems and Management P 16 PDF Archived from the original PDF on 3 October 2011 Retrieved 25 April 2011 DeLong 1998 Wong and Iverson 2004 BC Ministry of Forests Research Program Seral Stages across forested landscapes 1998 Intact Forest Landscapes intactforests org a b c d Intact Forest Landscapes Greenpeace International Archived from the original on 18 May 2020 BOREALFOREST ORG Boreal Forests of the World Introduction borealforest org 30 August 2022 Sources edit nbsp This article incorporates text from a free content work Licensed under CC BY SA 3 0 license statement permission Text taken from Global Forest Resources Assessment 2020 Key findings FAO FAO nbsp This article incorporates text from a free content work Licensed under CC BY SA 3 0 license statement permission Text taken from The State of the World s Forests 2020 In brief Forests biodiversity and people FAO amp UNEP FAO amp UNEP Further reading editProvincial Old Growth regulations of British Columbia Canada Old Growth Forest Definitions from U S Regional Ecosystem Office Collection of Google map links of clear cuts in or around old growth Managing for Biodiversity in Young Forests U S Geological Survey Biological Science Report pdf The State of British Columbia s Forests Third Edition BC Journal of Ecosystems Old growth definitions and management A literature review Natural Resources Canada Old growth boreal forests unraveling the mysteries permanent dead link External links edit nbsp Wikimedia Commons has media related to Primeval forests Our disappearing forests Archived 24 September 2008 at the Wayback Machine Rainforest Action Network Ancient Forest Exploration amp Research Natural Resources Canada 2003 Old Growth Forest Definitions for Ontario Submissions to XII World Forest Congress 2003 Minnesota Department of Natural Resources Archived 17 May 2019 at the Wayback Machine Archangel Ancient Tree Archive Old Growth Trees Portal nbsp Environment Retrieved from https en wikipedia org w index php title Old growth forest amp oldid 1189242264, wikipedia, wiki, book, books, library,

article

, read, download, free, free download, mp3, video, mp4, 3gp, jpg, jpeg, gif, png, picture, music, song, movie, book, game, games.