Deforestation Changing Agricultural Management Climate Change

Total Page:16

File Type:pdf, Size:1020Kb

Deforestation Changing Agricultural Management Climate Change Orchid Conservation Orchid conservation facts • There are 26,000 known orchid species and an estimated 5,000 still to be discovered. Around 200-300 are discovered each year and most unknown species are likely to be found in the Andes. • Around 33% of orchid species are thought to be threatened but less than 1% (206 species) have been formally assessed. In contrast, all 10,000 known bird species have been assessed. • This map shows the ‘biodiversity hotspots’; areas with at least 1,500 unique plant species and over 70% loss of natural habitats. Major centres of orchid diversity broadly correspond with these highly threatened hotspots. • Orchids are under threat from both general factors that affect all species, such as habitat loss and climate change, and specific threats that target certain species, such as over-collection for trade. General threats to orchids Deforestation Climate Change Around 75% of orchid species grow Climate change may result in as epiphytes, many of them in tropical migration of species to cooler areas, forests. The loss of these habitats is most likely towards the poles or to occurring on a large scale due to a higher elevations. Mountain species combination of conversion of land to and those in areas surrounded by agricultural or development use, degraded or lost habitats will not be forest fires or logging for timber. able to migrate and will be at risk of extinction. Even where movement is • Many species in Nigeria and possible, orchids and their specific Cameroon, such as Bulbophyllum pollinators may move at different bifarium, are threatened due to rates or may become out of sync clearance of land for agriculture2 with each other, decreasing the chance of pollination. • In Ecuador, species such as Cattleya maxima are being • For every 1oC increase in spring threatened as the trees that they temperature, Ophrys sphegodes grow on are felled. flowers in the UK open around 6 days earlier5 • Orchids in the Seychelles, such Cattleya maxima growing on a tree in a deforested landscape in Ecuador. Photo: Dave Roberts as Malaxis seychellarum may be threatened by a reduction of cloud forest humidity due to climate change6 Orchids growing on a tree in a mountainous area of Ecuador. Photo: Ian Chalmers Changing agricultural management For terrestrial orchids, destruction for development is not the only threat. Many orchids grow well in agricultural landscapes but can decline following changes caused by intensification, abandonment of traditional practices or changing grazing or burning regimes. • Terrestrial species in Greece and Turkey may be threatened by the abandonment of traditional olive groves and pastoral activities3 • In the USA, Platanthera praeclara is threatened by a shift away from traditional prairie management, which has led to trampling by cattle and out-competition by invasive plant species4 Orchis anatolica, growing in Turkey. Photo: Susanne Masters 1Joppa, L.N., Roberts, D.L., Myers, N., Pimm, S.L. (2011) Biodiversity hotspots house most undiscovered plant species. Proceedings of the National Academy of Sciences, 108: 13171-13176. 2Pollard, B.J. & Darbyshire, I. 2004. Bulbophyllum bifarium. In: IUCN 2012. IUCN Red List of Threatened Species. Version 2012.2. www.iucnredlist.org accessed 31st March 2013 3Rankou, H. 2011. Anacamptis boryi. In: IUCN 2012. IUCN Red List of Threatened Species. Version 2012.2. www.iucnredlist.org accessed 31st March 2013 4Goedeke, T., Sharma, J., Delphey, P. & Marshall Mattson, K. 2008. Platanthera praeclara. In: IUCN 2012. IUCN Red List of Threatened Species. Version 2012.2. www.iucnredlist.org accessed 31st March 2013 5Robbirt, K.M., Davy, A.J., Hutchings, M.J., Roberts, D.L. (2011) Validation of biological collections as a source of phenological data for use in climate change studies: a case study with the orchid Ophrys sphegodes. Journal of Ecology, 99:235-241. 6Gerlach, J. 2011. Malaxis seychellarum. In: IUCN 2012. IUCN Red List of Threatened Species. Version 2012.2. www.iucnredlist.org accessed 31st March 2013 Bulbophyllum species growing in an ex situ conservation centre in Malaysia. Photo: Amy Hinsley Why conserve orchids in the wild? Whilst ex situ orchid conservation in seed banks, botanical gardens and nurseries is important, it is essential that species are also conserved in situ in their natural habitats. This is especially important as successful reintroductions of orchids in to the wild are difficult to achieve, due to the different selection pressures that exist in cultivation. They are indicator species As they often rely on specific conditions, including the presence of certain pollinators and fungi, orchids are amongst the first species to be lost when an ecosystem is under stress. This makes them good ‘indicator’ species, providing a valuable early warning for the declining health of an ecosystem and allowing conservation action to be taken before it is too late. This is especially true of Other species may rely on them epiphytes1 but terrestrial orchids can also be used in this Ecosystems consist of complex interrelationships and way, such as the white-fringed orchid Platanthera sometimes the loss of one species may result in the decline blephariglottis in Canada, which is a good indicator for in others. This may be especially true for orchids, due to sphagnum bog health2 their specific relationships with other species. For example, it has been suggested that the brazil nut tree relies on the female of one or two orchid bee species for pollination. The male bees, in turn, rely on certain orchids, from which they collect fragrance chemicals that they use to attract their mates. Without the orchid, the bees would not be able to breed, there would be no pollinator for the tree and there would be no more brazil nuts3 There may be more than we think The diversity of wild orchids is far greater than those in cultivation, and wild populations provide important genetic storehouses that have the potential to produce new varieties, including new colours that may be popular in trade. As well as new forms there are likely to be many more species; between 200-300 are still being discovered each year4. Research suggests that many unknown species will be in the most threatened areas5, meaning that without conservation it is likely that we may lose new varieties and species before they are even discovered. They may be important to local communities Orchids provide a source of food, medicine and decoration to people who live near to their habitats and may also be used in religious or cultural ceremonies, such as Day of the Dead in Mexico. Where orchids are in demand from trade, their collection may also provide money to communities, as can promoting orchids in their natural habitats as tourist attractions. Using orchids as a tourist attraction can encourage the long term protection of wider orchid habitats. In this way, orchids can act as a ‘flagship’ for the conservation of a habitat, such as in the case of the Tanzanian Southern Highlands, a National Park designated based solely on the orchids it contains6. 1Turner, I.M., Tan, H.T.W., Wee, Y.C., Ibrahim, A. B., Chew, P.T. and Corlett, R.T. (1994), A Study of Plant Species Extinction in Singapore: Lessons for the Conservation of Tropical Biodiversity. Conservation Biology, 8: 705–712. 2Laroche, V., Pellerin, S., & Brouillet, L. (2012). White Fringed Orchid as indicator of Sphagnum bog integrity. Ecological Indicators, 14(1), 50-55. 3Mori, S. A., Prance, G. T., & Balick, M. J. (1990). Taxonomy, ecology, and economic botany of the Brazil nut (Bertholletia excelsa Humb. & Bonpl.: Lecythidaceae). Advances in Economic Botany, 8, 130-150. 4Royal Botanic Gardens, Kew. http://www.kew.org/plants/orchids/orchiddiscovery.html. Accessed March 2013. 5Joppa, L.N., Roberts, D.L., Myers, N., Pimm, S.L. (2011) Biodiversity hotspots house most undiscovered plant species. Proceedings of the National Academy of Sciences, 108: 13171-13176. A wild Cypripedium growing in China. Photo: Dave Roberts 6Davenport, T. R., & Ndangalasi, H. J. (2003). An escalating trade in orchid tubers across Tanzania's Southern Highlands: assessment, dynamics and conservation implications. Oryx, 37(01), 55-61. .
Recommended publications
  • Seed Ecology Iii
    SEED ECOLOGY III The Third International Society for Seed Science Meeting on Seeds and the Environment “Seeds and Change” Conference Proceedings June 20 to June 24, 2010 Salt Lake City, Utah, USA Editors: R. Pendleton, S. Meyer, B. Schultz Proceedings of the Seed Ecology III Conference Preface Extended abstracts included in this proceedings will be made available online. Enquiries and requests for hardcopies of this volume should be sent to: Dr. Rosemary Pendleton USFS Rocky Mountain Research Station Albuquerque Forestry Sciences Laboratory 333 Broadway SE Suite 115 Albuquerque, New Mexico, USA 87102-3497 The extended abstracts in this proceedings were edited for clarity. Seed Ecology III logo designed by Bitsy Schultz. i June 2010, Salt Lake City, Utah Proceedings of the Seed Ecology III Conference Table of Contents Germination Ecology of Dry Sandy Grassland Species along a pH-Gradient Simulated by Different Aluminium Concentrations.....................................................................................................................1 M Abedi, M Bartelheimer, Ralph Krall and Peter Poschlod Induction and Release of Secondary Dormancy under Field Conditions in Bromus tectorum.......................2 PS Allen, SE Meyer, and K Foote Seedling Production for Purposes of Biodiversity Restoration in the Brazilian Cerrado Region Can Be Greatly Enhanced by Seed Pretreatments Derived from Seed Technology......................................................4 S Anese, GCM Soares, ACB Matos, DAB Pinto, EAA da Silva, and HWM Hilhorst
    [Show full text]
  • Native Orchids of Oklahoma Dr. Lawrence K. Magrath Curator-USAO
    Oklahoma Native Plant Record 39 Volume 1, Number 1, December 2001 Native Orchids of Oklahoma Dr. Lawrence K. Magrath Curator-USAO (OCLA) Herbarium Chickasha, OK 73018-5358 As of the publication of this paper Oklahoma is known to have orchids of 33 species in 18 genera, which compares to 20 species and 11 genera reported by Waterfall (1969). Four of the 33 species are possibly extinct in the state based on current survey work. The greatest concentration of orchid species is in the southeastern corner of the state (Atoka, Bryan, Choctaw, LeFlore, McCurtain and Pushmataha Counties). INTRODUCTION Since the time of Confucius (551-479 BCE) who mentioned lan in his writings, "acquaintance with The family Orchidaceae is the largest of the good men was like entering a room full of lan or families of flowering plants with somewhere between fragrant orchids" (Withner, 1959), orchids have been 25,000 and 35,000 species, with new species important in many facets of Chinese life including continually being described. There are also literature, painting, horticulture, and not least, numerous natural and artificial hybrids. The only medicine". They are mentioned in the materia place where orchids are not known to occur is medica, “Sheng nung pen ts'ao ching”, tracing back Antarctica. to the legendary emperor Sheng Nung (ca. 28th Orchids fascinate us because of the century BCE). The term "lan hua" in early Chinese seemingly infinite combinations of colors and forms records refers to species of the genus Cymbidium that are found in orchid flowers from the Arctic to (Withner, 1959), most likely Cymbidium the tropical rain forests.
    [Show full text]
  • Platanthera Chapmanii: Culture, Population Augmentation, and Mycorrhizal Associations
    Platanthera chapmanii: culture, population augmentation, and mycorrhizal associations By Kirsten Poff, B.S. A Thesis In Plant and Soil Science Submitted to the Graduate Faculty of Texas Tech University in Partial Fulfillment of the Requirements for the Degree of MASTER OF SCIENCE Approved Dr. Jyotsna Sharma Chair of Committee Dr. Scott Longing Dr. John Zak Dr. Mark Sheridan Dean of the Graduate School August, 2016 © 2016, Kirsten Poff Texas Tech University, Kirsten Poff, August 2016 ACKNOWLEDGEMENTS First I would like to thank my mentor and advisor, Dr. Jyotsna Sharma for all of her help and support. She has challenged and encouraged me throughout my program and the duration of this project. Thanks to her, I am light-years ahead of where I was two years ago. Texas Parks and Wildlife is also gratefully acknowledged for funding portions of this study. I also wish to express my gratitude to Dr. John Zak for his enthusiasm and for encouraging my love of microbes. I also gratefully thank Dr. Scott Longing for his advice, and constructive comments. I sincerely thank all three committee members for all the time and energy they have spent on me throughout the duration of my project. I gratefully acknowledge Dr. Jason Woodward for his encouragement and recommendations as well. I also acknowledge Dr. Cynthia McKenney and Mr. Russel Plowman for their support; I now have a passion for teaching, and a much better understanding of what it is like to teach college level courses. I want to also thank Mr. Robby Carlson for his time and technological assistance.
    [Show full text]
  • Iowa Habitat Loss and Disappearing Wildlife Iowa Habitat Loss and Disappearing Wildlife
    Iowa Habitat Loss and Disappearance IowaAssociationofNaturalists Iowa Environmental Issues Series Iowa Habitat Loss and Disappearing Wildlife Iowa Habitat Loss and Disappearing Wildlife Habitat and wildlife Iowa habitat owa was once a land dominated by prairie and scattered prairie I wetlands. Thick woodlands and forested wetlands bordered its rivers and streams and covered the rugged landscape of northeast Iowa. The numerous interior streams meandered their way to the great border rivers - the Mississippi and the Missouri. Since Euro-American settlement, however, the historic Iowa landscape has been drastically changed, replaced by farms, towns, and highways. The once dominant Iowa prairie has been reduced to Iowa’s most rare and endangered habitat. Habitat refers to the features of an area that allow a wildlife species to live there. Although some types of wildlife may have many specific habitat needs, all wildlife have four basic habitat requirements: • adequate supplies of the right types of food; • available structure and materials that provide shelter to serve as safe places to live and raise young; • accessible and adequate supplies of water; and • enough space to find these necessary resources and to exercise natural behavior. When a wildlife species can no longer find enough food, water, shelter, or space, its habitat has been lost. Wildlife habitat is lost when land is cleared, polluted, or otherwise altered. IowaAssociationofNaturalists 1 Iowa Habitat Loss and Disappearing Wildlife Habitat is often described in terms of biological communities or habitat types. In addition to prairies, other habitat types include woodlands, wetlands, and waterways such as rivers and streams. Like prairies, these habitat types also have been lost or altered.
    [Show full text]
  • Do You Know Platanthera Praeclara?
    University of Nebraska - Lincoln DigitalCommons@University of Nebraska - Lincoln Proceedings of the North American Prairie Conferences North American Prairie Conference 1989 Do You Know Platanthera praeclara? Rochelle Bjugstad Moon Meadows Road, Rapid City, South Dakota Ardell J. Bjugstad Rocky Mountain Forest and Range Experiment Station, USDA, Forest Service, Rapid City, South Dakota Follow this and additional works at: https://digitalcommons.unl.edu/napcproceedings Part of the International and Area Studies Commons Bjugstad, Rochelle and Bjugstad, Ardell J., "Do You Know Platanthera praeclara?" (1989). Proceedings of the North American Prairie Conferences. 14. https://digitalcommons.unl.edu/napcproceedings/14 This Article is brought to you for free and open access by the North American Prairie Conference at DigitalCommons@University of Nebraska - Lincoln. It has been accepted for inclusion in Proceedings of the North American Prairie Conferences by an authorized administrator of DigitalCommons@University of Nebraska - Lincoln. DO YOU KNOW PLATANTHERA PRAECLARA? Rochelle Bjugstad Moon Meadows Road, Rapid City, South Dakota 57701 and Ardell J. Bjugstad Rocky Mountain Forest and Range Experiment Station, USDA, Forest Service, Rapid City, South Dakota 57701 Abstract. This is a brief synthesis on the plant, habitat and range of the the nectar tube 3.5- 5 em, and the main petals 1.5-2.5 cm. Western western prairie fringed orchid (Platanthera praeclara Sheviak and Bowles). prairie fringed orchid capsules are produced after flowering and This species was once common in the tall grass prairie, but its numbers have been greatly reduced by improper management and loss of habitat. remain in the pod until it drys, cracks, and tiny seeds are dispersed.
    [Show full text]
  • Ja Roheka Käokeele (Platanthera Chlorantha) Levik Ning Kaitse Eestis Lõputöö Liina Sirel
    Tartu Ülikool Kahelehise käokeele (Platanthera bifolia) ja roheka käokeele (Platanthera chlorantha) levik ning kaitse Eestis Lõputöö Liina Sirel Juhendaja: teadur Silvia Pihu Kaitsmisele lubatud: Juhendaja: /allkiri, kuupäev/ Osakonna juhataja: /allkiri, kuupäev/ Tartu 2013 SISUKORD 1. SISSEJUHATUS ....................................................................................................... 3 2. MATERJAL JA METOODIKA ................................................................................ 4 3. KAHELEHINE JA ROHEKAS KÄOKEEL ............................................................. 5 3.1. Käokeelte üldiseloomustus ................................................................................. 5 3.2. Käokeelte morfoloogilised tunnused ja Eesti liikide eristamine ........................ 6 3.3. Kahelehise ja roheka käokeele levik Eestis ........................................................ 7 3.4. Kahelehise ja roheka käokeele bioloogia ja paljunemine................................. 11 3.5. Käokeelte ohustatus ja kaitse (Eestis) .............................................................. 13 4. ARUTELU ............................................................................................................... 15 KOKKUVÕTE ................................................................................................................ 16 SUMMARY .................................................................................................................... 17 TÄNUAVALDUSED ....................................................................................................
    [Show full text]
  • Pollination of Western Prairie Fringed Orchid, Platanthera Praeclara Sheviak & Bowles: Implications for Restoration and Management
    Pollination of Western Prairie Fringed Orchid, Platanthera praeclara Sheviak & Bowles: implications for restoration and management Laura Phillips Introduction The beautiful western prairie fringed orchid, Platanthera praeclara, was once widespread in the tallgrass prairies across the upper Midwest (Sheviak and Bowles 1986). As Europeans settled North America, they discovered the fertile soils that lay beneath tallgrass prairies and began converting these vast grasslands into agricultural cropland. Some prairie lands were spared the plow only to be altered instead by suppression of the historic fire regimes that had maintained the prairie community for thousands of years. Today, only one percent of original tallgrass prairie remains, mostly in small, relatively isolated fragments, often surrounded by agricultural lands and urban development, and many are further threatened by invasion of non-native species and native woody species that now thrive in the fire-free environment (Kline 1997). Many of the unique plant species of the tallgrass prairie community, including P. praeclara, have also suffered great population declines in response to the loss of suitable habitat. The western and eastern prairie fringed orchids, P. praeclara and P. leucophaea, have declined by more than 70%, according to original county records (Bowles 1983), and therefore in 1989 they were listed as a federally threatened species under the Endangered Species Act (U.S. Fish and Wildlife Service 1996). Habitat loss is considered the greatest threat to the prairie fringed orchids, therefore current management plans focus primarily on maintaining quality prairie habitat using standard restoration techniques, such as burning and mowing (U.S. Fish and Wildlife Service 1996). Although the survival of P.
    [Show full text]
  • WILDLIFE in a CHANGING WORLD an Analysis of the 2008 IUCN Red List of Threatened Species™
    WILDLIFE IN A CHANGING WORLD An analysis of the 2008 IUCN Red List of Threatened Species™ Edited by Jean-Christophe Vié, Craig Hilton-Taylor and Simon N. Stuart coberta.indd 1 07/07/2009 9:02:47 WILDLIFE IN A CHANGING WORLD An analysis of the 2008 IUCN Red List of Threatened Species™ first_pages.indd I 13/07/2009 11:27:01 first_pages.indd II 13/07/2009 11:27:07 WILDLIFE IN A CHANGING WORLD An analysis of the 2008 IUCN Red List of Threatened Species™ Edited by Jean-Christophe Vié, Craig Hilton-Taylor and Simon N. Stuart first_pages.indd III 13/07/2009 11:27:07 The designation of geographical entities in this book, and the presentation of the material, do not imply the expressions of any opinion whatsoever on the part of IUCN concerning the legal status of any country, territory, or area, or of its authorities, or concerning the delimitation of its frontiers or boundaries. The views expressed in this publication do not necessarily refl ect those of IUCN. This publication has been made possible in part by funding from the French Ministry of Foreign and European Affairs. Published by: IUCN, Gland, Switzerland Red List logo: © 2008 Copyright: © 2009 International Union for Conservation of Nature and Natural Resources Reproduction of this publication for educational or other non-commercial purposes is authorized without prior written permission from the copyright holder provided the source is fully acknowledged. Reproduction of this publication for resale or other commercial purposes is prohibited without prior written permission of the copyright holder. Citation: Vié, J.-C., Hilton-Taylor, C.
    [Show full text]
  • Publications1
    PUBLICATIONS1 Book Chapters: Zettler LW, J Sharma, and FN Rasmussen. 2003. Mycorrhizal Diversity (Chapter 11; pp. 205-226). In Orchid Conservation. KW Dixon, SP Kell, RL Barrett and PJ Cribb (eds). 418 pages. Natural History Publications, Kota Kinabalu, Sabah, Malaysia. ISBN: 9838120782 Books and Book Chapters Edited: Sharma J. (Editor). 2010. North American Native Orchid Conservation: Preservation, Propagation, and Restoration. Conference Proceedings of the Native Orchid Conference - Green Bay, Wisconsin. Native Orchid Conference, Inc., Greensboro, North Carolina. 131 pages, plus CD. (Public Review by Dr. Paul M. Catling published in The Canadian Field-Naturalist Vol. 125. pp 86 - 88; http://journals.sfu.ca/cfn/index.php/cfn/article/viewFile/1142/1146). Peer-reviewed Publications (besides Journal publications or refereed proceedings) Goedeke, T., Sharma, J., Treher, A., Frances, A. & *Poff, K. 2016. Calopogon multiflorus. The IUCN Red List of Threatened Species 2016: e.T64175911A86066804. https://dx.doi.org/10.2305/IUCN.UK.2016- 1.RLTS.T64175911A86066804.en. Treher, A., Sharma, J., Frances, A. & *Poff, K. 2015. Basiphyllaea corallicola. The IUCN Red List of Threatened Species 2015: e.T64175902A64175905. https://dx.doi.org/10.2305/IUCN.UK.2015- 4.RLTS.T64175902A64175905.en. Goedeke, T., Sharma, J., Treher, A., Frances, A. & *Poff, K. 2015. Corallorhiza bentleyi. The IUCN Red List of Threatened Species 2015: e.T64175940A64175949. https://dx.doi.org/10.2305/IUCN.UK.2015- 4.RLTS.T64175940A64175949.en. Treher, A., Sharma, J., Frances, A. & *Poff, K. 2015. Eulophia ecristata. The IUCN Red List of Threatened Species 2015: e.T64176842A64176871. https://dx.doi.org/10.2305/IUCN.UK.2015- 4.RLTS.T64176842A64176871.en.
    [Show full text]
  • Western Prairie Fringed Orchid: a Threatened Midwestern Prairie Plant.” Minnesota Department of Natural Resources, St
    Note: This digital document was adapted from Sather, N. 1991. “Western prairie fringed orchid: a threatened midwestern prairie plant.” Minnesota Department of Natural Resources, St. Paul. 14 pages. WESTERN PRAIRIE FRINGED ORCHID A THREATENED MIDWESTERN PRAIRIE PLANT Photo by G. N. Rysgaard What is Western Prairie Fringed Orchid? The Western prairie fringed orchid (Platanthera praeclara) is a federally threatened prairie wildflower presently known to occur in 7 states and one Canadian province. It was first documented by the Lewis and Clark expedition (under the name Habenaria leucophaea) apparently in what is now Wyoming, but the heart of its apparent historic range was from the Red River valley of Manitoba, Minnesota, and North Dakota, extending southeastward to Iowa and Missouri and westward to northeastern Oklahoma, eastern Kansas, central Nebraska and eastern South Dakota. Western prairie fringed orchid occurs most often in remnant native prairies and meadows, but has also been observed at disturbed sites. In the southern part of its range it is more likely to be found in mesic upland prairies and in the north more frequently in wet prairies and sedge meadows. It is also known from prairies and swales in sand dune complexes that are fed by shallow underground water. What does the Western Prairie Fringed Orchid look like? The federally protected Western prairie fringed orchid is a stout, erect, long-lived perennial with a showy open raceme (spike) of up to two dozen white to creamy white flowers often an inch or more in size, each with a long nectar spur. The sepals are tinged with pale green.
    [Show full text]
  • Western Prairie Fringed-Orchid (Platanthera Praeclara) in Canada
    PROPOSED Species at Risk Act Recovery Strategy Series Recovery Strategy for the Western Prairie Fringed-orchid (Platanthera praeclara) in Canada Western Prairie Fringed-orchid © Manitoba Conservation July 2006 About the Species at Risk Act Recovery Strategy Series What is the Species at Risk Act (SARA)? SARA is the Act developed by the federal government as a key contribution to the common national effort to protect and conserve species at risk in Canada. SARA came into force in 2003, and one of its purposes is “to provide for the recovery of wildlife species that are extirpated, endangered or threatened as a result of human activity.” What is recovery? In the context of species at risk conservation, recovery is the process by which the decline of an endangered, threatened, or extirpated species is arrested or reversed and threats are removed or reduced to improve the likelihood of the species’ persistence in the wild. A species will be considered recovered when its long-term persistence in the wild has been secured. What is a recovery strategy? A recovery strategy is a planning document that identifies what needs to be done to arrest or reverse the decline of a species. It sets goals and objectives and identifies the main areas of activities to be undertaken. Detailed planning is done at the action plan stage. Recovery strategy development is a commitment of all provinces and territories and of three federal agencies — Environment Canada, Parks Canada Agency, and Fisheries and Oceans Canada — under the Accord for the Protection of Species at Risk. Sections 37–46 of SARA (http://www.sararegistry.gc.ca/the_act/default_e.cfm) outline both the required content and the process for developing recovery strategies published in this series.
    [Show full text]
  • Biogeography and Ecology of Tulasnellaceae
    Chapter 12 Biogeography and Ecology of Tulasnellaceae Franz Oberwinkler, Darı´o Cruz, and Juan Pablo Sua´rez 12.1 Introduction Schroter€ (1888) introduced the name Tulasnella in honour of the French physicians, botanists and mycologists Charles and Louis Rene´ Tulasne for heterobasidiomycetous fungi with unique meiosporangial morphology. The place- ment in the Heterobasidiomycetes was accepted by Rogers (1933), and later also by Donk (1972). In Talbot’s conspectus of basidiomycetes genera (Talbot 1973), the genus represented an order, the Tulasnellales, in the Holobasidiomycetidae, a view not accepted by Bandoni and Oberwinkler (1982). In molecular phylogenetic studies, Tulasnellaceae were included in Cantharellales (Hibbett and Thorn 2001), a position that was confirmed by following studies, e.g. Hibbett et al. (2007, 2014). 12.2 Systematics and Taxonomy Most tulasnelloid fungi produce basidiomata on wood, predominantly on the underside of fallen logs and twigs. Reports on these collections are mostly published in local floras, mycofloristic listings, or partial monographic treatments. F. Oberwinkler (*) Institut für Evolution und O¨ kologie, Universita¨tTübingen, Auf der Morgenstelle 1, 72076 Tübingen, Germany e-mail: [email protected] D. Cruz • J.P. Sua´rez Museum of Biological Collections, Section of Basic and Applied Biology, Department of Natural Sciences, Universidad Te´cnica Particular de Loja, San Cayetano Alto s/n C.P, 11 01 608 Loja, Ecuador © Springer International Publishing AG 2017 237 L. Tedersoo (ed.), Biogeography of Mycorrhizal Symbiosis, Ecological Studies 230, DOI 10.1007/978-3-319-56363-3_12 238 F. Oberwinkler et al. Unfortunately, the ecological relevance of Tulasnella fruiting on variously decayed wood or on bark of trees is not understood.
    [Show full text]