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Associations

provided by BioImages, the virtual fieldguide, UK
In Great Britain and/or Ireland:
Plant / associate
fruitbody of Armillaria ectypa is associated with Sphagnum

Plant / associate
fruitbody of Arrhenia epichysium is associated with Sphagnum

Plant / associate
fruitbody of Arrhenia obscurata is associated with Sphagnum
Other: minor host/prey

Plant / associate
fruitbody of Arrhenia onisca is associated with Sphagnum
Other: major host/prey

Plant / associate
fruitbody of Arrhenia philonotis is associated with Sphagnum

Plant / associate
fruitbody of Arrhenia sphagnicola is associated with gametophyte of Sphagnum

Plant / associate
fruitbody of Arrhenia velutipes is associated with gametophyte of Sphagnum

Plant / epiphyte
sporangium of Badhamia lilacina grows on gametophyte of Sphagnum

Plant / resting place / among
imago of Bagous frit may be found among plants of Sphagnum

Foodplant / saprobe
gregarious apothecium of Byssonectria fusispora is saprobic on burnt peat of Sphagnum
Other: major host/prey

Plant / associate
fruitbody of Collybia dryophila is associated with Sphagnum
Other: minor host/prey

Plant / associate
fruitbody of Entoloma atromarginatum is associated with Sphagnum

Plant / associate
fruitbody of Entoloma cuspidiferum is associated with Sphagnum

Plant / associate
fruitbody of Entoloma elodes is associated with Sphagnum

Plant / associate
fruitbody of Entoloma fuscomarginatum is associated with live Sphagnum

Plant / associate
fruitbody of Entoloma jennyae is associated with Sphagnum

Plant / associate
fruitbody of Entoloma rhombisporum var. rhombisporum is associated with Sphagnum

Plant / associate
fruitbody of Entoloma sphagneti is associated with dying Sphagnum

Plant / associate
fruitbody of Entoloma sphagnorum is associated with Sphagnum

Plant / associate
fruitbody of Entoloma turci is associated with Sphagnum
Other: minor host/prey

Plant / resting place / within
nest of Formica transkaucasica may be found in bogs of Sphagnum
Other: sole host/prey

Plant / associate
fruitbody of Galerina atkinsoniana is associated with Sphagnum

Plant / associate
fruitbody of Galerina paludosa is associated with live Sphagnum
Remarks: season: 5-8

Plant / associate
fruitbody of Galerina septentrionalis is associated with Sphagnum

Plant / associate
fruitbody of Galerina sphagnorum is associated with Sphagnum

Plant / associate
fruitbody of Galerina stordalii is associated with Sphagnum

Plant / associate
fruitbody of Galerina tibiicystis is associated with Sphagnum

Plant / associate
sporocarp of Glomus fuegianum is associated with Sphagnum
Other: major host/prey

Plant / associate
fruitbody of Hebeloma atrobrunneum is associated with Sphagnum
Other: major host/prey

Plant / associate
fruitbody of Hygrocybe coccineocrenata is associated with live Sphagnum

Plant / associate
fruitbody of Hygrocybe turunda is associated with live Sphagnum
Other: minor host/prey

Plant / epiphyte
solitary apothecium of Hymenoscyphus vasaensis grows on leaf of Sphagnum

Plant / associate
fruitbody of Hypholoma elongatum is associated with Sphagnum

Plant / associate
fruitbody of Hypholoma udum is associated with Sphagnum

Plant / associate
fruitbody of Inocybe pallida is associated with Sphagnum

Plant / associate
fruitbody of Lactarius lacunarum is associated with Sphagnum

Plant / associate
fruitbody of Lactarius musteus is associated with Sphagnum

Plant / associate
fruitbody of Lactarius sphagneti is associated with Sphagnum

Plant / associate
fruitbody of Lactarius vietus is associated with Sphagnum

Plant / associate
fruitbody of Leccinum aerugineum is associated with Sphagnum

Plant / associate
fruitbody of Leccinum holopus is associated with Sphagnum

Plant / grows among
sessile apothecium of Leucoscypha erminea grows among gametophyte of Sphagnum
Remarks: season: 6
Other: minor host/prey

Plant / grows among
apothecium of Leucoscypha leucotricha grows among gametophyte of Sphagnum
Other: minor host/prey

Plant / resting place / on
Botrydina anamorph of Lichenomphalia umbellifera may be found on plant of Sphagnum
Other: minor host/prey

Foodplant / pathogen
fruitbody of Loreleia postii infects and damages moribund thallus of Sphagnum

Plant / associate
fruitbody of Mycena adonis var. adonis is associated with Sphagnum
Other: minor host/prey

Plant / associate
fruitbody of Mycena capillaripes is associated with Sphagnum
Other: minor host/prey

Plant / associate
fruitbody of Mycena megaspora is associated with Sphagnum
Other: minor host/prey

Plant / resting place / within
nest of Myrmica scabrinodis may be found in bogs of Sphagnum

Plant / associate
fruitbody of Naucoria sphagneti is associated with Sphagnum

Plant / associate
fruitbody of Omphalina fulvopallens is associated with Sphagnum

Plant / grows among
apothecium of Pezoloma ciliifera grows among gametophyte of Sphagnum

Plant / associate
apothecium of Pezoloma iodocyanescens is associated with gametophyte of Sphagnum

Plant / associate
fruitbody of Phaeogalera stagnina is associated with Sphagnum
Other: major host/prey

Plant / resting place / within
puparium of Phaonia jaroschewskii may be found in Sphagnum

Plant / associate
fruitbody of Psathyrella ploddensis is associated with Sphagnum

Plant / associate
fruitbody of Psathyrella sphagnicola is associated with Sphagnum

Plant / grows among
gregarious apothecium of Pseudoplectania sphagnophila grows among gametophyte of Sphagnum

Plant / associate
fruitbody of Russula aquosa is associated with Sphagnum

Plant / associate
fruitbody of Russula claroflava is associated with Sphagnum

Plant / associate
fruitbody of Russula emetica is associated with Sphagnum

Plant / associate
fruitbody of Russula sphagnophila is associated with Sphagnum

Plant / grows among
apothecium of Sarcoleotia turficola grows among gametophyte of Sphagnum

Plant / associate
fruitbody of Sphagnomphalia brevibasidiata is associated with Sphagnum

Plant / associate
fruitbody of Tephrocybe palustris is associated with Sphagnum

Plant / associate
fruitbody of Trechispora byssinella is associated with live plant of Sphagnum

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Brief Summary

provided by EOL authors
Sphagnum is a genus that comprises one of the major groups (superclasses) of the largest phylum of mosses (Bryophyta) generally found in boreal areas in the Northern Hemisphere (although diverse species also occur in tropical and subtropical areas, and in the Southern Hemisphere), best known as a typical species of bogs, coniferous swamps, and fens, and used horticulturally (as a plant growing medium or soil amendment), as a biofuel (traditional in Ireland), and to flavor alcoholic beverages (whisky and Scotch), among other products. The Sphagnum genus contains roughly 135 species, although classifications have varied considerably in the number of species recognized. All species display a distinctive branch arrangement, with 3 or more fascicles (groups) of branches produced with every 4th leaf. Within a fascicle, at least 2 branches hang downwards, pressed close to the stem, while 1 to 3 are held out, diverging from the stem. Sphagnum mosses are a dominant component of bogs and other wetland ecosystems, and affect important ecological processes. They tend to acidify their environment, and thus to direct future succession. The presence of Sphagnum deposits and spores has been used in paleoecological studies as an indicator of past climates and ecological conditions. This group of mosses has a tremendous water-holding capacity, potentially retaining 25 times their dry weight in water, which modifies spring runoff in vast stretches of permafrost in the Arctic; however, when permafrost melts, the Sphagnum becomes saturated and may suddenly release large volumes of water. Sphagnum, often referred to as peat or peat moss (although “peat” includes various species of partly decayed vegetation), is widely used in horticulture, as a planting medium, mulch, soil conditioner, and for grafting trees and cultivating mushrooms. However, nearly half of the peat harvested annually is used for fuel; it is an important fuel source in northern European countries including Finland, Germany, Ireland, Poland, Russia, and Sweden. Peat may be burned directly or converted to other burnable fuels, including methane, ethylene, natural or synthetic gas. Sphagnum is also used as fiber or pulp for paper manufacture, and is a component of recently developed construction materials, including “peatcrete” (peat mixed with concrete, then pressed with Portland cement and water and cast or molded) and “peatwood” (mixed with phenolic resin and molded). Sphagnum peatlands have been used for wastewater treatment. When sewage is discharged to an active peatland, Sphagnum can absorb toxic heavy metals, oil spills, PCP (pentachlorophenol), microbes, and excess nitrogen and potassium from eutrophic river water. Sphagnum has also been used in diverse ways in the past. Native Americans used it for diapers, and it was used during World War I in bandages instead of cotton—both applications took advantage of its absorbency, but also its antimicrobial and antiviral properties, which have been confirmed in recent studies. It has been used to stuff mattresses, pillows, furnishings, and as insulation, and in sanitary napkins and boot liners (to absorb moisture and odors), as animal bedding, or mixed with molasses as livestock feed. It can be mixed with alkaline to produce a brown dye. Scotch and Irish whisky are flavored by peat when germinated malt (or barley) is dried over peat fires. Threats to Sphagnum peatlands are outlined in the “Threats” section. (Anderson et al. 2009, Crandall-Stotler and Bartholomew-Began 2007, Crum 1988, Crum and Anderson 1981, Glime 2007, McQueen and Andrus 2007, Wikipedia 2012.)
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Threats

provided by EOL authors
Sphagnum peatlands are threatened by overharvesting, conversion to agricultural land, hydrological changes from aquifers altered by irrigation or overuse, and damage from forest harvesting and air pollution. Sphagnum is often considered a renewable resource that can be “harvested,” because raking after partial harvest can encourage regeneration. However, much peat harvesting, especially that for peat used as fuel, is actually mining—characterized by a complete removal of all peat layers, so that the Sphagnum cannot regenerate. Even if some Sphagnum is left during harvest, and hydrological conditions are not irrevocably altered, the moss regenerates slowly, with its peat accumulating at 10 to 40 cm (4 to 13 in) per thousand years, so it cannot be harvested again in a lifetime. In some countries, overharvesting threatens Sphagnum peatlands—Finland, for example, is estimated to have lost 60% of its Sphagnum peatlands. Overharvesting may pose the largest threat, but destruction of aquifers that feed peatland can pose a particularly dramatic one. When hydrological alterations or extreme drought dry out a peatland, the decomposing peat can generate methane and other flammable gases that collect in underground pockets. When ignited by lightening strikes, or auto-ignited through the combination of combustible gases, this can lead to subterranean fires that can extend to large areas of peatland, and may burn for weeks to months or years, resulting in massive releases of the CO2 that is stored in these deposits. Such fires have affected large peatlands in Indonesia, as well as a peatland in Spain that is part of a nature reserve listed on the Ramsar convention. Although it is not clear that these peatlands were Sphagnum dominated, these cases suggest the potential threats to any peatland from widespread hydrological changes. Some studies suggest that Sphagnum is particularly sensitive to damage from air pollution, and may decline with acid rain or increased ozone. (Anderson et al. 2009, Crandall-Stotler and Bartholomew-Began 2007, Crum 1988, Crum and Anderson 1981, Glime 2007, Lopez-Gunn et al. 2011, McQueen and Andrus 2007, Wikipedia 2012.)
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Sphagnum

provided by wikipedia EN

Sphagnum is a genus of approximately 380 accepted species[2][3] of mosses, commonly known as sphagnum moss, also bog moss and quacker moss (although that term is also sometimes used for peat). Accumulations of Sphagnum can store water, since both living and dead plants can hold large quantities of water inside their cells; plants may hold 16 to 26 times as much water as their dry weight, depending on the species.[4] The empty cells help retain water in drier conditions.

As Sphagnum moss grows, it can slowly spread into drier conditions, forming larger mires, both raised bogs and blanket bogs.[5] Thus, Sphagnum can influence the composition of such habitats, with some describing Sphagnum as 'habitat manipulators'.[6] These peat accumulations then provide habitat for a wide array of peatland plants, including sedges and ericaceous shrubs, as well as orchids and carnivorous plants.[7][8]

Sphagnum and the peat formed from it do not decay readily because of the phenolic compounds embedded in the moss's cell walls. In addition, bogs, like all wetlands, develop anaerobic soil conditions, which produces slower anaerobic decay rather than aerobic microbial action. Peat moss can also acidify its surroundings by taking up cations, such as calcium and magnesium, and releasing hydrogen ions.

Under the right conditions, peat can accumulate to a depth of many meters. Different species of Sphagnum have different tolerance limits for flooding and pH, and any one peatland may have a number of different Sphagnum species.[9][7]

Sphagnum structure

An individual Sphagnum plant consists of a main stem, with tightly arranged clusters of branch fascicles usually consisting of two or three spreading branches and two to four hanging branches. The top of the plant (capitulum) has compact clusters of young branches that give the plant it's characteristic tuft-like appearance. Along the stem are scattered leaves of various shapes, named stem leaves; the shape varies according to species.

Cellular structure

Sphagnum cells

Sphagnum has a distinctive cellular structure. The stem portion consists of two important sections. The pith which is the site of food production and storage, and the cortical layer which serves to absorb water and protect the pith. Mosses have no vascular system to move water and nutrients around the plant. Thus tissues are thin and usually one cell thick to allow them to diffuse easily. Sphagnum mosses have two distinct cell types. There are small, green, living cells with chlorophyll (chlorophyllose cells) that produce food for the plant. Additionally there are larger hyaline or retort cells that are barrel shaped and have a pore at one end to allow for water absorption and improved water-holding capacity. These unique cells help Sphagnum to retain water during prolonged UV exposure.[10]

Lifecycle

Sphagnum, like all other land plants, has an alternation of generations; like other bryophytes, the haploid gametophyte generation is dominant and persistent. Unlike other mosses, the long-lived gametophytes do not rely upon rhizoids to assist in water uptake.[4]

Sphagnum species can be unisexual (male or female, dioecious) or bisexual (male and female gametes produced from the same plant; monoecious); In North America, 80% of Sphagnum species are unisexual.[11]

Gametophytes have substantial asexual reproduction by fragmentation, producing much of the living material in sphagnum peatlands.[12]

Swimming sperm fertilize eggs contained in archegonia that remain attached to the female gametophyte. The sporophyte is relatively short-lived, and consists almost entirely of a shiny green, spherical spore capsule that becomes black with spores. Sporophytes are raised on stalks to facilitate spore dispersal, but unlike other mosses, Sphagnum stalks are produced by the maternal gametophyte. Tetrahedral haploid spores are produced in the sporophyte by meiosis, which are then dispersed when the capsule explosively discharges its cap, called an operculum, and shoots the spores some distance. The spores germinate to produce minute protonemae, which start as filaments, can become thalloid, and can produce a few rhizoids. Soon afterwards, the protonema develops buds and these differentiate into its characteristic, erect, leafy, branched gametophyte with chlorophyllose cells and hyaline cells.[13] This stage dominates the environment where Sphagnum grows, obliterating and burying the protonema and eventually building up into layers of dead moss called peat.

Carpets of living Sphagnum may be attacked by various fungi, and one fungus that is also a mushroom, Sphagnurus paluster, produces conspicuous dead patches. When this fungus and other agarics attack the protonema, Sphagnum is induced to produce nonphotosynthetic gemmae that can survive the fungal attack and months later germinate to produce new protonema and leafy gametophytes.[14] It is unknown whether the leafy stage can produce such gemmae.

Taxonomy and phylogeny

Peat moss can be distinguished from other moss species by its unique branch clusters. The plant and stem color, the shape of the branch and stem leaves, and the shape of the green cells are all characteristics used to identify peat moss to species. Sphagnum taxonomy has been very contentious since the early 1900s; most species require microscopic dissection to be identified. In the field, most Sphagnum species can be identified to one of four major sections of the genus—classification and descriptions follow Andrus 2007 (Flora North America):[11]

Red sphagnum closeup
  • Sphagnum sect. Acutifolia plants generally form hummocks above the water line, usually colored orange or red. Examples: Sphagnum fuscum and Sphagnum warnstorfii.
  • Sphagnum sect. Cuspidata plants are usually found in hollows, lawns, or are aquatic, and are green. Examples: Sphagnum cuspidatum and Sphagnum flexuosum.
  • Sphagnum sect. Sphagnum plants have the largest gametophytes among the sections, forming large hummocks, their leaves form cuculate (hood-shaped) apices, and are green, except for Sphagnum magellanicum Example: Sphagnum austinii.
  • Sphagnum sect. Subsecunda plants vary in color from green to yellow and orange (but never red), and are found in hollows, lawns, or are aquatic. Species always with unisexual gametophytes. Examples: Sphagnum lescurii and Sphagnum pylaesii.

The reciprocal monophyly of these sections and two other minor ones (Rigida and Squarrosa) has been clarified using molecular phylogenetics.[15] All but two species normally identified as Sphagnum reside in one clade; two other species have recently been separated into new families within the Sphagnales reflecting an ancestral relationship with the Tasmanian endemic Ambuchanania and long phylogenetic distance to the rest of Sphagnum.[16] Within main clade of Sphagnum, phylogenetic distance is relatively short, and molecular dating methods suggest nearly all current Sphagnum species are descended from a radiation that occurred just 14 million years ago.[17]

Geographic distribution

Sphagnum with northern pitcher plants (Sarracenia purpurea) at Brown's Lake Bog, Ohio

Sphagnum mosses occur mainly in the Northern Hemisphere in peat bogs, conifer forests, and moist tundra areas. Their northernmost populations lie in the archipelago of Svalbard, Arctic Norway, at 81° N.[18]

In the Southern Hemisphere, the largest peat areas are in southern Chile and Argentina, part of the vast Magellanic moorland (circa 44,000 square km; 17,000 sq. mi.).[19] Peat areas are also found in New Zealand and Tasmania. In the Southern Hemisphere, however, peat landscapes may contain many moss species other than Sphagnum. Sphagnum species are also reported from "dripping rocks" in mountainous, subtropical Brazil.[20]

Spore dispersal

As with many other mosses, Sphagnum species disperse spores through the wind. The tops of spore capsules are only about 1 cm (12") above ground, and where wind is weak. As the spherical spore capsule dries, the operculum is forced off, followed by a cloud of spores. The exact mechanism has traditionally attributed to a "pop gun" method using air compressed in the capsule, reaching a maximum velocity of 3.6 meters (12') per second,[21] but alternative mechanisms have been recently proposed.[22] High-speed photography has shown vortex rings are created during the discharge, which enable the spores to reach a height of 10 to 20 cm (4" to 8"), further than would be expected by ballistics alone. The acceleration of the spores is about 36,000G.[23][24] Spores are extremely important in establishment of new populations in disturbed habitats and on islands.[25]

Human activities like slash-and-burn and cattle grazing are believed to promote the growth and expansion of Sphagnum moss. Oceanic islands such as the Faroe Islands, the Galápagos or the Azores have recorded a significant increase in their Sphagnum populations after human settlement.[26][27]

Uses

Peat moss soil amendment, made of partly decayed, dried sphagnum moss

Decayed, dried sphagnum moss has the name of peat or peat moss. This is used as a soil conditioner which increases the soil's capacity to hold water and nutrients by increasing capillary forces and cation exchange capacity – uses that are particularly useful in gardening. This is often desired when dealing with very sandy soil, or plants that need increased or steady moisture content to flourish. A distinction is sometimes made between sphagnum moss, the live moss growing on top of a peat bog, and 'sphagnum peat moss' (North American usage) or 'sphagnum peat' (British usage), the latter being the slowly decaying matter underneath.[28]

Dried sphagnum moss is used in northern Arctic regions as an insulating material.

Anaerobic acidic sphagnum bogs have low rates of decay, and hence preserve plant fragments and pollen to allow reconstruction of past environments.[8] They even preserve human bodies for millennia; examples of these preserved specimens are Tollund Man, Haraldskær Woman, Clonycavan Man and Lindow Man. Such bogs can also preserve human hair and clothing, one of the most noteworthy examples being Egtved Girl, Denmark. Because of the acidity of peat, however, bones are dissolved rather than preserved. These bogs have also been used to preserve food.[29] Up to 2000-year-old containers of butter or lard have been found.[30]

Sphagnum moss wound dressings being made at the University of Toronto c. 1914

Sphagnum moss has been used for centuries as a dressing for wounds, including through World War I.[4][31] Preparations using Sphagnum such as Sphagnol soap have been used for various skin conditions including acne, ringworm, and eczema. The soap was used by the British Red Cross during both World Wars to treat facial wounds and trench sores.[32]

Since it is absorptive and extremely acidic, it inhibits growth of bacteria and fungi, so it is used for shipping seeds and live plants.

Peat moss is used to dispose of the clarified liquid output (effluent) from septic tanks in areas that lack the proper conditions for ordinary disposal means. It is also used as an environmentally friendly alternative to chlorine in swimming pool sanitation.[33] The moss inhibits the growth of microbes and reduces the need for chlorine in swimming pools.[34]

In Finland, peat mosses have been used to make bread during famines.[35]

Long strand Sphagnum moss used in mounting a Vanda Falcata orchid

In China, Japan and Korea, long strand dried sphagnum moss is traditionally used as a potting medium for cultivating Vanda falcata orchids.[36]

Conservation

Mer Bleue Conservation Area, a large, protected Sphagnum bog near Ottawa, Ontario, Canada

Several of the world's largest wetlands are sphagnum-dominated bogs, including the West Siberian Lowland, the Hudson Bay Lowland and the Mackenzie River Valley. These areas provide habitat for common and rare species. They also store large amounts of carbon, which helps reduce global warming.[37]

According to an article written in 2013, the U.S. got up to 80% of sphagnum peat moss it uses from Canada. At that time, in Canada, the peat bog mass harvested each year was roughly 1/60th of the peat mass that annually accumulated. About 0.02% of the 1.1 million km2 (422,000 square miles) of Canadian peat bog are used for peat moss mining.[38] Some efforts are being made to restore peat bogs after peat mining, and some debate exists as to whether the peat bogs can be restored to their premining condition and how long the process takes. "The North American Wetlands Conservation Council estimates that harvested peatlands can be restored to 'ecologically balanced systems' within five to 20 years after peat harvesting." Some wetlands scientists assert that "a managed bog bears little resemblance to a natural one. Like tree farms, these peatlands tend toward monoculture, lacking the biodiversity of an unharvested bog."[39]

PittMoss, a peat moss alternative made from recycled newspaper, has emerged as a sustainable substitute in growing media.[40] Coir has also been touted as a sustainable alternative to peat moss in growing media.[41] Another peat moss alternative is manufactured in California from sustainably harvested redwood fiber. Semi-open cell polyurethane materials available in flaked and sheet stock are also finding application as sphagnum replacements with typical usage in green wall and roof garden substrates.[42]

Chile

In the 2010s, Sphagnum peat in Chile has begun to be harvested at a large scale for export to countries like Japan, South Korea, Taiwan and the United States. Given Sphagnum’s property to absorb excess water and release it during dry months harvesting of Sphagnum, means that overexploitation may threaten the water supply in the fjords and channels of Chile.[43] Extraction of Sphagnum in Chile is regulated by law since 2 August 2018.[44] Since 2018 Chilean law allows only for the manual extraction of Sphagnum using only pitchforks or similar tools as an aid.[45] In a given area (polygon) at least 30% of Sphagnum coverage has to be left unharvested.[45] Harvested Sphagnum fibers may not exceed 15 cm (6") in length and the remaining Sphagnum after harvest may never have a length less than 5 cm (2") over the water table.[45] In the regions of Los Ríos (40°S) and Los Lagos (41–43°S) the same plots may be harvested after 12 years, while further south in Aysén (44–48°S) and Magallanes (49–56°S) 85 years have to pass before the same area is harvested again.[45]

Harvesting aside, bogs where Sphagnum grows have also come under threat by the development of wind farms in cool humid areas such as the Cordillera del Piuchén where the San Pedro Wind Farm was constructed in the 2010s.[46] The construction of each wind turbine usually implies the removal of vegetation and the alteration of the soil, changing by the way also of the local hydrology.[46]

Europe

Europe has a long history of the exploitation of peatlands. The Netherlands, for example, once had large areas of peatland, both fen and bog. Between 100 AD and the present, they were drained and converted to agricultural land.[8]: Fig. 14.2  The English broadlands have small lakes that originated as peat mines.[47] More than 90% of the bogs in England have been damaged or destroyed.[48][49] A handful of bogs has been preserved through government buyouts of peat-mining interests.[50] Over longer time scales, however, some parts of England, Ireland, Scotland, and Wales have seen expansion of bogs, particularly blanket bogs, in response to deforestation and abandonment of agricultural land.[8]: Fig. 11.8 

New Zealand

New Zealand has, like other parts of the world, lost large areas of peatland. The latest estimates for wetland loss in New Zealand are 90% over 150 years.[51] In some cases, better care is taken during the harvesting of Sphagnum to ensure enough moss is remaining to allow regrowth. An 8-year cycle is suggested, but some sites require a longer cycle of 11 to 32 years for full recovery of biomass, depending on factors including whether reseeding is done, the light intensity, and the water table.[52] This "farming" is based on a sustainable management program approved by New Zealand's Department of Conservation; it ensures the regeneration of the moss, while protecting the wildlife and the environment. Most harvesting in New Zealand swamps is done only using pitchforks without the use of heavy machinery. During transportation, helicopters are commonly employed to transfer the newly harvested moss from the swamp to the nearest road.

References

  1. ^ Tropicos, Isocladus Lindb.
  2. ^ "Dierk Michaelis (2019): The Sphagnum Species of the World (Sphagnum bible: keys for all peat moss species by continents, and Sphagnum species lists for 20 phytogeographic regions of the world)". Schweizerbart. 21 November 2019.
  3. ^ "Sphagnum on theplantlist". Theplantlist.org. Retrieved 17 September 2016.
  4. ^ a b c Bold, H. C. 1967. Morphology of Plants. second ed. Harper and Row, New York. p. 225-229.
  5. ^ Gorham E. (1957). "The development of peatlands". Quarterly Review of Biology. 32 (2): 145–66. doi:10.1086/401755. S2CID 129085635.
  6. ^ Walker, M. D. 2019. Sphagnum: the biology of a habitat manipulator. Sicklebrook Publishing, Sheffield, U.K.
  7. ^ a b O'Neill, Alexander; et al. (25 February 2020). "Establishing Ecological Baselines Around a Temperate Himalayan Peatland". Wetlands Ecology & Management. 28 (2): 375–388. doi:10.1007/s11273-020-09710-7. S2CID 211081106.
  8. ^ a b c d Keddy, P. A. (2010). Wetland Ecology: Principles and Conservation (2nd edition). Cambridge University Press, Cambridge, UK. 397 pp.
  9. ^ Vitt D. H., Slack N. G. (1984). "Niche diversification of Sphagnum relative to environmental factors in northern Minnesota peatlands". Canadian Journal of Botany. 62 (7): 1409–30. doi:10.1139/b84-192.
  10. ^ "Morphology of the Sphagnopsida". ucmp.berkeley.edu. Retrieved 6 April 2023.
  11. ^ a b Andrus, Richard. Sphagnum. Flora of North America. 2007
  12. ^ Rydin, Hakan and Jeglum, John K. 2006. Biology of Peatlands. Oxford University Press, Oxford.
  13. ^ Schofield, W. B. 1985. Introduction to Bryology. Macmillan Publ. Co., N.Y. & London
  14. ^ Redhead, S.A. (1981). "Parasitism of bryophytes by agarics". Can. J. Bot. 59 (1): 63–67. doi:10.1139/b81-011.
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Sphagnum: Brief Summary

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Sphagnum is a genus of approximately 380 accepted species of mosses, commonly known as sphagnum moss, also bog moss and quacker moss (although that term is also sometimes used for peat). Accumulations of Sphagnum can store water, since both living and dead plants can hold large quantities of water inside their cells; plants may hold 16 to 26 times as much water as their dry weight, depending on the species. The empty cells help retain water in drier conditions.

As Sphagnum moss grows, it can slowly spread into drier conditions, forming larger mires, both raised bogs and blanket bogs. Thus, Sphagnum can influence the composition of such habitats, with some describing Sphagnum as 'habitat manipulators'. These peat accumulations then provide habitat for a wide array of peatland plants, including sedges and ericaceous shrubs, as well as orchids and carnivorous plants.

Sphagnum and the peat formed from it do not decay readily because of the phenolic compounds embedded in the moss's cell walls. In addition, bogs, like all wetlands, develop anaerobic soil conditions, which produces slower anaerobic decay rather than aerobic microbial action. Peat moss can also acidify its surroundings by taking up cations, such as calcium and magnesium, and releasing hydrogen ions.

Under the right conditions, peat can accumulate to a depth of many meters. Different species of Sphagnum have different tolerance limits for flooding and pH, and any one peatland may have a number of different Sphagnum species.

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