Sphagnum

Sphagnum
Sphagnum flexuosum
Scientific classification
Kingdom: Plantae
Phylum: Bryophyta
Class: Sphagnopsida
Subclass: Sphagnidae
Order: Sphagnales
Family: Sphagnaceae
Genus: Sphagnum
L.
Species

List of Sphagnum species

Synonyms[1]

Isocladus Lindb.

Sphagnum is a genus of approximately 120 species[2] of mosses, commonly known as peat moss. Accumulations of Sphagnum can store water, since both living and dead plants can hold large quantities of water inside their cells; plants may hold 16–26 times as much water as their dry weight, depending on the species.[3] The empty cells help retain water in drier conditions. Hence, as sphagnum moss grows, it can slowly spread into drier conditions, forming larger mires, both raised bogs and blanket bogs.[4] 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.[5] 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, so any one peatland may have a number of different Sphagnum species.[6]

Individual peat moss plants consist 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, or capitulum, has compact clusters of young branches. Along the stem are scattered leaves of various shapes, named stem leaves; the shape varies according to species. The leaves consist of two kinds of cells; small, green, living cells (chlorophyllose cells), and large, clear, structural, dead cells (hyaline cells). The latter have the large water-holding capacity.

Life cycle

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.[3] 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.[7] Gametophytes have substantial asexual reproduction by fragmentation, producing much of the living material in sphagnum peatlands.[8] 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.[9] 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 non-photosynthetic gemmae that can survive the fungal attack and months later germinate to produce new protonema and leafy gametophytes.[10] 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):

Red sphagnum closeup

The reciprocal monophyly of these sections and two other minor ones (Rigida and Squarrosa) has been clarified using molecular phylogenetics.[11] All but two species normally identified as Sphagnum reside in one clade; two other species have recently been separated into new families within the Sphagnaceae reflecting an ancestral relationship with the Tasmanian endemic Ambuchanania and long phylogenetic distance to the rest of Sphagnum.[12] 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.[13]

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.

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).[14] 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.[15]

Spore dispersal

As with many other mosses, Sphagnum species disperse spores through the wind. The tops of spore capsules are only about 1 cm 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 per second,[16] but alternative mechanisms have been recently proposed.[17] 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, further than would be expected by ballistics alone. The acceleration of the spores is about 36,000G.[18][19] Spores are extremely important in establishment of new populations in disturbed habitats and on islands.[20]

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. This is often necessary 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.[21]

Dried sphagnum moss is also 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.[5] 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.[22] Up to 2000-year-old containers of butter or lard have been found.[23]

Sphagnum moss has also been used for centuries as a dressing for wounds, including through World War I.[3][24] 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.[25] The moss inhibits the growth of microbes and reduces the need for chlorine in swimming pools.[26]

In New Zealand, both the species S. cristatum and S. subnitens are harvested by hand and exported worldwide for use as hanging basket liners, as a growing medium for young orchids, and mixed with other potting mixes to enhance their moisture retaining value.

Peat moss is a critical element for growing mushrooms. The fungal mycelium grows in compost with a layer of peat moss on top, through which the mushrooms come out, a process called casing.

Peat moss, dead or alive, is also a very important soil and topper for most carnivorous plants.

In the 7th Framework Programme Mossclone peat mosses multiplied in moss bioreactors are developed as a new tool to monitor air pollution.

Sphagnum is also used in air layering, a method of propagation used to propagate woody stems like guavas. A ball of Sphagnum is tied against a midway ringed bark of a branch still attached on the parent plant using a translucent plastic material (vitalon).

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 for rare species. They also store large amounts of carbon, which helps reduce global warming.[27]

The U.S. gets up to 80% of sphagnum peat moss it uses from Canada. In Canada, it has been estimated that new peat bog mass accumulates 60 times faster than the amount harvested each year. Approximately .02 percent of the 270 million acres (422,000 square miles) of Canadian peat bog are used for peat moss mining.[28] There are some efforts made to restore peat bogs after peat mining. There is some debate as to whether the peat bogs can be restored to their pre-mining condition and how long the process takes. ″The North American Wetlands Conservation Council estimates that harvested peatlands can be restored to ′ecologically balanced systems′ – if not peat bogs – 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 un- harvested bog.″[29]

PittMoss, a peat moss alternative made from recycled newspaper, has emerged as a sustainable substitute in growing media.[30] Coir has also been touted as a sustainable alternative to peat moss in growing media.[31] 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.[32]

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.[5]:Fig. 14.2 The English broadlands have small lakes that originated as peat mines.[33] More than 90% of the bogs in England have been damaged or destroyed.[34][35] A handful of bogs have been preserved through government buyouts of peat-mining interests.[36] 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.[5]: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.[37] In some cases, better care is taken during the harvesting of Sphagnum to ensure enough moss is remaining to allow regrowth. An eight-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, light intensity, and the water table.[38] 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. ↑ "Sphagnum on theplantlist". Theplantlist.org. Retrieved 2013-09-11.
  3. 1 2 3 Bold, H.C. 1967. Morphology of Plants. second ed. Harper and Row, New York. p. 225-229.
  4. ↑ Gorham, E. (1957). The development of peatlands. Quarterly Review of Biology, 32, 145–66.
  5. 1 2 3 4 Keddy, P.A. (2010). Wetland Ecology: Principles and Conservation (2nd edition). Cambridge University Press, Cambridge, UK. 497 pp.
  6. ↑ Vitt, D. H. and Slack, N. G. (1984). Niche diversification of Sphagnum relative to environmental factors in northern Minnesota peatlands. Canadian Journal of Botany, 62, 1409–30.
  7. ↑ Andrus, Richard. Sphagnum. Flora of North America. 2007
  8. ↑ Rydin, Hakan and Jeglum, John K. 2006. Biology of Peatlands. Oxford University Press, Oxford.
  9. ↑ Schofield, W. B. 1985. Introduction to Bryology. Macmillan Publ. Co., N.Y. & London
  10. ↑ Redhead, S.A. (1981). "Parasitism of bryophytes by agarics". Canad. Jour. Bot. 59 (1): 63–67. doi:10.1139/b81-011.
  11. ↑ Shaw, A.J.; Cox, C.; Boles, S.B. (2003). "Polarity of peatmoss (Sphagnum) evolution: who says bryophytes have no roots?". American Journal of Botany 90 (12): 1777–1787. doi:10.3732/ajb.90.12.1777.
  12. ↑ Shaw, A.J. et al. Newly resolved relationships in an early land plant lineage: Bryophyta class Sphagnopsida (peat mosses) American Journal of Botany 97: 1511-1531 (2010)
  13. ↑ Shaw, A.J. et al. Peatmoss (Sphagnum) diversification associated with Miocene Northern Hemisphere climatic cooling? Molecular Phylogenetics and Evolution Volume 55, Issue 3, June 2010, Pages 1139-1145.
  14. ↑ Arroyo, M.T.K., P. Mihoc, P. Pliscoff and M. Arroyo-Kalin. (2005). The Magellanic moorland. P. 424-445 in L.H. Fraser and P.A. Keddy (eds.). The World’s Largest Wetlands: Ecology and Conservation. Cambridge University Press, Cambridge, UK.
  15. ↑ Crum, H. (1991). Two new species of Sphagnum from Brazil. The Bryologist 94: 301-303.
  16. ↑ Sebastian Sundberg (2010). "Size matters for violent discharge height and settling speed of Sphagnum spores: important attributes for dispersal potential". Annals of Botany 105 (2): 291–300. doi:10.1093/aob/mcp288. PMC 2814761. PMID 20123930.
  17. ↑ Jeff Duckett; Pressel, Silvia; P’ng, Ken M. Y.; Renzaglia, Karen S. (2009). "Exploding a myth: the capsule dehiscence mechanism and the function of pseudostomata in Sphagnum". New Phytologist 183 (4): 1053–63. doi:10.1111/j.1469-8137.2009.02905.x. PMID 19552695.
  18. ↑ Johan L. van Leeuwen (July 23, 2010). "Launched at 36,000g". Science 329 (5990): 395–6. doi:10.1126/science.1193047. PMID 20651138.
  19. ↑ Dwight L. Whitaker and Joan Edwards (July 23, 2010). "Sphagnum Moss Disperses Spores with Vortex Rings". Science 329 (5990): 406. doi:10.1126/science.1190179. PMID 20651145.
  20. ↑ Sundberg, S (2005). "Larger capsules enhance short-range spore dispersal in Sphagnum, but what happens further away?". Oikos 108 (1): 115–124. doi:10.1111/j.0030-1299.2005.12916.x.
  21. ↑ Hood, Gerry (January, 1995). "Don't Confuse Sphagnum Moss with Peat Moss". African Violet Magazine, p. 34
  22. ↑ Madrigal, Alexis. Bogosphere: The Strangest Things Pulled Out of Peat Bogs. Wired Magazine. 21 Aug. 2009
  23. ↑ Bog Butter Test. New Scientist. 20 March 2004.
  24. ↑ "Facts about Peat Moss (Sphagnum) - Encyclopedia of Life". Eol.org. Retrieved 2013-09-11.
  25. ↑ Moss Proving An Alternative To Chlorine In Pools. WCCO. 15 Aug. 2008.
  26. ↑ Hill, Catey. Time to fire the pool boy? Moss helps pools stay clean. Daily News. 29 Oct. 2009.
  27. ↑ Fraser, L.H. and P.A. Keddy (eds.). 2005. The World’s Largest Wetlands: Ecology and Conservation. Cambridge University Press, Cambridge, UK. 488 p.
  28. ↑ Trail, Jesse Vernon. The truth about peat moss. The Ecologist. 25 Jan. 2013.
  29. ↑ Priesnitz, Wendy. Ask Natural Life: Does Peat Moss Have a Place In the Ecological Garden. Natural Life Magazine. 1 Jul. 2012.
  30. ↑ Cellulose Based Soil Medium as a Peat Moss Substitute EPA/SBIR Sponsored (Contract No. 68D60035)(C) 1997 Wabash Vallet Products, Inc. Crown Point, Indiana.
  31. ↑ Richards, Davi. Coir is sustainable alternative to peat moss in the garden. Oregon State University Extension Service.
  32. ↑ Raviv, Michael. Soilless Culture: Theory and Practice: Theory and Practice. Elsevier.
  33. ↑ Moss, B. (1984). Medieval man-made lakes: progeny and casualties of English social history, patients of twentieth century ecology. Transactions of the Royal Society of South Africa, 45, 115–28.
  34. ↑ Insight into threatened peat bogs. BBC News.
  35. ↑ The RSPB: Policy
  36. ↑ Jeffery, Simon. Bogs to be preserved for peat's sake. The Guardian. 27 Feb. 2002.
  37. ↑ Peters, M. and Clarkson, B. 2010. Wetland Restoration: A Handbook for New Zealand Freshwater Systems. Manaaki Whenua Press, Lincoln, N.Z. ISBN 978-0-478-34707-4 (online)
  38. ↑ Sphagnum research programme: the ecological effects of commercial harvesting Department of Conservation R.P. Buxton, P.N. Johnson and P.R. Espie. Wellington, N.Z. Department of Conservation, 1996 ISBN 0478017871 http://www.doc.govt.nz/documents/science-and-technical/sfc025.pdf (Retrieved 10 January 2013)

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