The Global Distribution of Freshwater Wetlands

Total Page:16

File Type:pdf, Size:1020Kb

The Global Distribution of Freshwater Wetlands NCAR/TN-416+STR NCAR TECHNICAL NOTE I - I September 1995 The Global Distribution of Freshwater Wetlands L. M. Stillwell-Soller L. F. Klinger D. Pollard S. L. Thompson CLIMATE AND GLOBAL DYNAMICS DIVISION I NATIONAL CENTER FOR ATMOSPHERIC RESEARCH BOULDER, COLORADO TABLE OF CONTENTS Page List of Tables . .. i List of Figures . .iv Preface .................. v Acknowledgments .... ............. .. .vi v. I Introduction .................... 1 II Scientific Rationale . .. 3 III Description of Data ..... .................... 5 IV Presentation of Figures . ............. ....... V Data Files ....... .. ...................... 9 References . .. 10 Table Captions . ..... ..... ....... 13 Figure Captions . .18 ii LIST OF TABLES Page Table 1. Aselman & Crutzen wetland categories ................ 14 Table 2. Aselman & Crutzen wetland category descriptions ......... 15 Table 3. Wetland categories used and corresponding data files ........ 16 Table 4. Bog and Fen vegetation types. ............. 17 iii LIST OF FIGURES Page0 Figure 1. Aselman & Crutzen's global distribution of wet-cultivation 20 rice paddies Figure 2. Aselman & Crutzen's monthly cultivated area of wet- 21 cultivation rice paddies for 10°latitude belts. Figure 3. Mid-range values for Aselman & Crutzen's wet-cultivation 22 rice paddy area. Figure 4. Distribution of total freshwater natural wetlands. 23 Figure 5. Distribution of wet-cultivation rice paddies. 23 Figure 6. Distribution of Fens. 24 Figure 7. Distribution of Bogs. 24 Figure 8. Distribution of Permanent Swamps. 25 Figure 9. Distribution of Permanent Marshes. 25 Figure 10. Distribution of Shallow Lakes 26 Figure 11. Distribution of Permanent Floodplains. 26 Figure 12. Distribution of Seasonal Floodplains 27 Figure 13. Distribution of Seasonal Swamps/Marshes. 27 Figures 14.a-14.1 Monthly distributions of Seasonal wet-cultivation Rice 28 Paddies. Figures 15.a-15.1 Monthly distribution of Seasonal Floodplains. 34 Figures 16.a-16.1 Monthly distribution of Seasonal Swamps/Marshes. 40 Figure 17. Seasonal Floodplains with unknown monthly variation. 46 Figure 18. Seasonal Swamps/Marshes with unknown monthly varia- 46 tion. Figure 19. Example of the ASCII text format for data files. 47 iv PREFACE During the last decade the complexity of land-surface models (LSMls) used in global climate models (GCMs) has increased dramatically, from soil buckets with prescribed albedos and surface roughness to explicit vegetation canopies overlying multi-layer soil profiles. Although the optimal levels of complexity for various global modeling applications are still unclear, some processes included in the newer LSMs can significantly affect GCM sensitivities at global and regional scales (e.g., Garratt, 1993; Henderson-Sellers et al., 1995; Pollard and Thompson, 1995). The added realism in the newer LSMs has created a need for global gridded datasets of various aspects of vegetation, soil and surface hydrology, in order to specify prescribed parameters in the models and to validate their predicted fields. One such set is the geographical and seasonal distribution of various types of wetlands. Although wetlands are not predicted or even prescribed yet in most LSMs, we anticipate that they will be included in the near future because of their importance to surface hydrology, trace gas fluxes, and the near-surface climate. To support this anticipated development we have assembled a global dataset of wetland distributions, using existing data sources and compiling them into a uniform set of digitized maps at 10x10 resolution for convenient use with GCMs. The main source for our dataset is Aselman and Crutzen (1989), who produced global maps of percent cover for a variety of wetlands categories. Their categories, which are physically based and well-suited for LSM applications, consist of Bogs, Fens, Permanent Swamps, Permanent Marshes, Shallow Lakes, Permanent Floodplains, Seasonal Floodplains, Seasonal Swamp/Marshes and Wet Rice Paddies. However, (i) their digitized files are not readily available, (ii) their seasonal information is coded in a relatively inconvenient way, and (iii) as discussed by Aselman and Crutzen, their data for Alaska is poor. We have partially remedied the latter drawback by merging their maps. with a recent dataset of Alaskan bogs and fens by Lee Klinger (NCAR, personal communication). This technical note describes procedures used to assemble our dataset, presents global maps of all the wetland categories, and provides some discussion of the importance of wetlands for climate studies. The complete set of digitized l°by 1° global maps is available by anonymous ftp and on the NCAR Mass Storage System, and information on the format and locations of these files is given below. v One drawback of the Aselman and Crutzen data is that salt marshes are not included because their original data was compiled specifically for the study of methane emissions which are dominated by freshwater sources. Cogley (1991) provides global maps of some types of salt water marshes and salt flats, but the overlap with the Aselman and Crutzen data is not entirely clear so we decided to omit this category and restrict our dataset to freshwater wetlands. Matthews and Fung (1987) have also compiled a global wetlands dataset by combining maps of soils, vegetation and inundation. However this indirect approach is relatively uncertain and indiscriminating compared to Aselman and Crutzen's and Klinger's direct approach of compiling local data sources. The two approaches and differences in their results are discussed by Aselman and Crutzen (1989). vi ACKNOWLEDGMENTS This work was conducted as part of the GENESIS Earth Systems Modeling Project at NCAR, supported by the U.S. Environmental Protection Agency Interagency Agreement No. DW49935658-01-0. We thank Dennis Shea, Gordon Bonan and Steve Hostetler for helpfull comments. vii I. Introduction. Historically, General Circulation Models (GCMs) treated surface processes rather simplistically as a result of technological and theoretical limitations. Consequently, detailed information regarding surface processes was not necessary for climate studies. With technological advancements, improved scientific knowledge and an increased awareness of the importance of surface processes upon the climate, GCM surface prescription capabilities became more sophisticated and better able to answer more complex climatological questions. As a result a need has arisen for accurate data bases containing necessary information about terrestrial systems. The global coverage and spatial distributions of vegetation types, soil types, and water sources are a few examples of the necessary surface information required for today's climate modeling studies. Other data needs are sure to arise as our understanding of land-atmosphere interactions, and their influence on the climate, improves. Past global climate simulations have demonstrated that the climate system is sensitive to relatively large changes in vegetation patterns and to the presence of water on the land surface (Charney, et al., 1977; Sud et al., 1990; Bonan et al., 1992). The distribution of wetlands is thus an important component of biosphere-atmosphere interactions because they embody both vegetation and freely available water. In addition, Wetland areas store and release atmospheric gases (CH4 and 002), decrease drainage and change surface albedos. For climate modeling, accurate estimates of the total land area coverage and the distribution of wetlands, as well as wetland types, are important if we are to understand methane flux characteristics from wetlands, wetland carbon storage dynamics and the effects of wetland hydrology on the climate system. This report describes a global wetland data base for climate modeling. Our aim is to provide an accurate, comprehensive and uniform set of files for convenient specification of wetlands in global climate models. The completed Wetlands data base consists of 68 ASCII data files, half (34) of which are gridded at a resolution of 2.5°by 5°and the other half gridded at a finer resolution of 1°by 1°. These data files are in the form of global maps showing the areal extent of land covered by different types of wetlands. The data base is essentially a re-gridding of Aselman and Crutzen's (1989) data base, with some reorganization for seasonally varying categories (henceforth, we refer to Aselman & 1 Crutzen as AC, and their 1989 paper as AC89). Alaskan data for bogs and fens provided by Dr. Lee Klinger (personal communication, 1995) are included because the AC data are relatively poor for Alaska (AC89). The remaining document is organized as follows: Section 2 includes a brief scientific discussion on the climatological importance of wetland areas, section 3 describes the original data and our data processing methods, section 4 presents the analyzed data in graphical form, and section 5 describes the data files, including file format, storage and access methods. 2 II. Scientific Rationale Wetlands alter the climate on global scales through the storage and release of greenhouse gases such as methane (CH4 ) and carbon dioxide (C0 2 ). Wetlands also moderate the climate on regional scales through hydrological processes such as increased evaporation and decreased drainage, and through an increase in the land albedo as compared to boreal forest zones (Klinger, 1991). The amount of methane gas in the atmosphere is increasing annually by approximately 1% (Matthews & Fung, 1987; AC89; Moore & Knowles, 1990). Several studies indicate that this
Recommended publications
  • Mangrove Swamp (Caroni Wetland, Trinidad)
    FIGURE 1.3 Swamps. (a) Floodplain swamp (Ottawa River, Canada). (b) Mangrove swamp (Caroni wetland, Trinidad). FIGURE 1.4 Marshes. (a) Riverine marsh (Ottawa River, Canada; courtesy B. Shipley). (b) Salt marsh (Petpeswick Inlet, Canada). FIGURE 1.5 Bogs. (a) Lowland continental bog (Algonquin Park, Canada). (b) Upland coastal bog (Cape Breton Island, Canada). FIGURE 1.6 Fens. (a) Patterned fen (northern Canada; courtesy C. Rubec). (b) Shoreline fen (Lake Ontario, Canada). FIGURE 1.7 Wet meadows. (a) Sand spit (Long Point, Lake Ontario, Canada; courtesy A. Reznicek). (b) Gravel lakeshore (Tusket River, Canada; courtesy A. Payne). FIGURE 1.8 Shallow water. (a) Bay (Lake Erie, Canada; courtesy A. Reznicek). (b) Pond (interdunal pools on Sable Island, Canada). FIGURE 2.1 Flooding is a natural process in landscapes. When humans build cities in or adjacent to wetlands, flooding can be expected. This example shows Cedar Rapids in the United States in 2008 (The Gazette), but incidences of flood damage to cities go far back in history to early cities such as Nineveh mentioned in The Epic of Gilgamesh (Sanders 1972). FIGURE 2.5 Many wetland organisms are dependent upon annual flood pulses. Animals discussed here include (a) white ibis (U.S. Fish and Wildlife Service), (b) Mississippi gopher frog (courtesy M. Redmer), (c) dragonfly (courtesy C. Rubec), and (d) tambaqui (courtesy M. Goulding). Plants discussed here include (e) furbish lousewort (bottom left; U.S. Fish and Wildlife Service) and ( f ) Plymouth gentian. -N- FIGURE 2.10 Spring floods produce the extensive bottomland forests that accompany many large rivers, such as those of the southeastern United States of America.
    [Show full text]
  • This Article Appeared in a Journal Published by Elsevier. the Attached
    This article appeared in a journal published by Elsevier. The attached copy is furnished to the author for internal non-commercial research and education use, including for instruction at the authors institution and sharing with colleagues. Other uses, including reproduction and distribution, or selling or licensing copies, or posting to personal, institutional or third party websites are prohibited. In most cases authors are permitted to post their version of the article (e.g. in Word or Tex form) to their personal website or institutional repository. Authors requiring further information regarding Elsevier’s archiving and manuscript policies are encouraged to visit: http://www.elsevier.com/copyright Author's personal copy Quaternary Research 75 (2011) 531–540 Contents lists available at ScienceDirect Quaternary Research journal homepage: www.elsevier.com/locate/yqres Response of a warm temperate peatland to Holocene climate change in northeastern Pennsylvania Shanshan Cai, Zicheng Yu ⁎ Department of Earth and Environmental Sciences, Lehigh University, 1 West Packer Avenue, Bethlehem, PA 18015, USA article info abstract Article history: Studying boreal-type peatlands near the edge of their southern limit can provide insight into responses of Received 11 September 2010 boreal and sub-arctic peatlands to warmer climates. In this study, we investigated peatland history using Available online 18 February 2011 multi-proxy records of sediment composition, plant macrofossil, pollen, and diatom analysis from a 14C-dated sediment core at Tannersville Bog in northeastern Pennsylvania, USA. Our results indicate that peat Keywords: accumulation began with lake infilling of a glacial lake at ~9 ka as a rich fen dominated by brown mosses.
    [Show full text]
  • Managing Iowa Habitats
    Managing Iowa Habitats Fen Wetlands Introduction Why should I be concerned? Fens are the rarest of Iowa’s wetland commu- Fens are an important and unique wetland nities and of great scientific interest. While type. Not only are the fens themselves rare, but their geology varies, they all are the products they shelter over 200 plant species, 20 of which of the seepage of groundwater to the surface. are Iowa endangered and threatened species. Because the water is rich in calcium and other Many of the plant species have been in these minerals, only a select group of plants is able to areas for thousands of years. The fen’s vegeta- grow there. As a result, fens contain many tion, in turn, shelters wildlife by providing plant species considered endangered or valuable habitat. threatened in Iowa. Fens are valuable to humans as well. They are A few of the oldest fens contain plant remains important as sites of groundwater discharge — that date back 10,000 years, though most Iowa good indicators of shallow aquifers. Vegetation fens are less than 5,000 years old. A few of in all wetlands plays an important role in these “younger” fens may have existed 10,000 recycling nutrients, trapping eroding soil, and years ago, but because of dramatic climate filtering out polluting chemicals such as changes, they may have dried up and lost the nitrates. However, the rarity of fens and their plant remains (by burning or erosion) that relatively small size makes it important could prove their age. When the climate grew to protect them from overloading by wetter again about 5,000 years ago, these fens these materials.
    [Show full text]
  • Northern Fen Communitynorthern Abstract Fen, Page 1
    Northern Fen CommunityNorthern Abstract Fen, Page 1 Community Range Prevalent or likely prevalent Infrequent or likely infrequent Absent or likely absent Photo by Joshua G. Cohen Overview: Northern fen is a sedge- and rush-dominated 8,000 years. Expansion of peatlands likely occurred wetland occurring on neutral to moderately alkaline following climatic cooling, approximately 5,000 years saturated peat and/or marl influenced by groundwater ago (Heinselman 1970, Boelter and Verry 1977, Riley rich in calcium and magnesium carbonates. The 1989). community occurs north of the climatic tension zone and is found primarily where calcareous bedrock Several other natural peatland communities also underlies a thin mantle of glacial drift on flat areas or occur in Michigan and can be distinguished from shallow depressions of glacial outwash and glacial minerotrophic (nutrient-rich) northern fens, based on lakeplains and also in kettle depressions on pitted comparisons of nutrient levels, flora, canopy closure, outwash and moraines. distribution, landscape context, and groundwater influence (Kost et al. 2007). Northern fen is dominated Global and State Rank: G3G5/S3 by sedges, rushes, and grasses (Mitsch and Gosselink 2000). Additional open wetlands occurring on organic Range: Northern fen is a peatland type of glaciated soils include coastal fen, poor fen, prairie fen, bog, landscapes of the northern Great Lakes region, ranging intermittent wetland, and northern wet meadow. Bogs, from Michigan west to Minnesota and northward peat-covered wetlands raised above the surrounding into central Canada (Ontario, Manitoba, and Quebec) groundwater by an accumulation of peat, receive inputs (Gignac et al. 2000, Faber-Langendoen 2001, Amon of nutrients and water primarily from precipitation et al.
    [Show full text]
  • FEN BOG from the Website North Yorkshire for the Book Discover Butterflies in Britain © D E Newland 2009
    FEN BOG from www.discoverbutterflies.com the website North Yorkshire for the book Discover Butterflies in Britain © D E Newland 2009 The North Yorkshire Moors Railway passes along the western edge of Fen Bog Fen Bog is 20 ha (50 acres) of This well-known site in TARGET SPECIES boggy marshland at the head Yorkshire is noted for its Large Heath (June and early of Newtondale, near Pickering many different species of July), Small Pearl-bordered in North Yorkshire. It is 3 butterflies, moths and and Dark Green Fritillaries; miles south of Goathland and dragonflies. There is a deep commoner species. lies on the route of the North bed of peat where many Yorkshire Moors Railway different bog plants flourish. It from Pickering to Grosmont. lies within a wide valley with heather, hard fern, mat grass and purple moor grass all growing stongly. The reserve is cared for by the Yorkshire Wildlife Trust. The North York Moors became one of our first National Parks in 1952. Its moors are one of the largest areas of heather moorland in Britain and cover an area of 550 square miles. It is hard to imagine that they were once permanently covered in ice and snow. When global warming took effect at the end of the Ice Age, the snowfields began to melt and melt water flowed south. It gouged out the deep valley of Newtondale where the Pickering Beck now flows. Newtondale runs roughly north-south parallel to the A169 Whitby to Pickering road and is a designated SSSI of 940 ha (2,300 acres).
    [Show full text]
  • Stow Cum Quy Fen Pond Survey
    Stow Cum Quy Fen pond survey A report for the Freshwater Habitats Trust July 2017 (Version 2) 1. Introduction Stow-cum-Quy Fen Site of Special Scientific Interest (SSSI) covers 29.6 hectares and is located 7.5 km north-east of the centre of Cambridge. It features a number of ponds, the largest being a coprolite pit from which phosphate-rich deposits were excavated in the mid to late 19th century for fertiliser (O’Connor, 2001 & 2011). Originally believed to be fossilised dinosaur dung, the ‘coprolite’ seams were in fact phosphatic nodules derived from the remains of marine molluscs, cephalopods and other organisms deposited during the Jurassic (Cambridgeshire Archaeology Field Group, 2015). The elongate shape of some smaller ponds suggests that these too originated as coprolite pits but others are likely to be stock watering ponds. This survey was commissioned by the Freshwater Habitats Trust as part of the Flagship Ponds project. Fieldwork for was undertaken by Jonathan Graham (botanical survey) and Martin Hammond (invertebrates) on 17th May 2017. This was followed by a second visit on 21st June 2017 to seek out additional species. 2. Survey methods Eight ponds (refer to location map below) were surveyed using PSYM (Predictive System for Multimetrics), the standard methodology for evaluating the ecological quality of ponds and small lakes (Environment Agency, 2002). A PSYM survey involves: Obtaining environmental data such as pond area, altitude, grid reference, substrate composition, cover of emergent vegetation, degree of shade, accessibility to livestock and water pH Collecting a sample of aquatic macro-invertebrates using a standard protocol (three minutes’ netting divided equally between each ‘meso-habitat’ within the pond basin, plus one minute searching the water surface and submerged debris) Recording wetland plants PSYM generates six ‘metrics’ (measurements) representing important indicators of ecological quality.
    [Show full text]
  • A Fen Is a Rare, Low Shrub- and Herb- Dominated Wetland That Is Fed by Calcareous Groundwater Seepage
    Habitat fact sheet Fen A fen is a rare, low shrub- and herb- dominated wetland that is fed by calcareous groundwater seepage. Fens almost always occur in areas influenced by carbonate bedrock (e.g., limestone and marble), and are identified by their low, often sparse vegetation and their distinctive plant community. Tussocky vegetation and small BellK. 2006 seepage rivulets are often present, and some fens have substantial areas of bare mineral Typical plants soil or organic muck. • Grasses and sedges such as spike-muhly, sterile sedge, porcupine sedge, yellow sedge, and woolly-fruit sedge • Shrubs including shrubby cinquefoil, K. BellK. 2007 alder-leaf buckthorn, and autumn willow Bog turtle • Wildflowers including grass-of- Parnassus and bog goldenrod Species of conservation concern Purple cliffbrake • More than 12 state-listed rare plants are found almost exclusively in fen habitats, including handsome sedge, Schweinitz’s sedge, bog valerian, scarlet Indian paintbrush, spreading globeflower, and swamp birch • Rare butterflies such as Dion skipper and black dash • Rare dragonflies such as forcipate emerald and Kennedy’s emerald • Bog turtle (Endangered in New York) • Spotted turtle, ribbon snake • Sedge wren, northern harrier These are just a few of the species of regional or statewide conservation concern that are known to occur in fen habitats. See Kiviat & Stevens (2001) Bell 2006 K. for a more extensive list. Fringed gentian Hudsonia Ltd. PO Box 5000, Annandale, NY 12504 (845) 758-7053 www.hudsonia.org Habitat fact sheet Page 2 Threats to fens Fens are highly vulnerable to degradation from direct disturbance and from activities in nearby upland areas.
    [Show full text]
  • New Orleans, LA USA
    July 28-August 1, 2014 | New Orleans, LA USA CEER 2014 Conference on Ecological and Ecosystem Restoration ELEVATING THE SCIENCE AND PRACTICE OF RESTORATION A Collaborative Effort of NCER and SER July 28-August 1, 2014 New Orleans, Louisiana, USA www.conference.ifas.ufl.edu/CEER2014 Welcome to the UF/IFAS OCI App! The University of Florida IFAS Office of Conferences & Institutes is happy to present a mobile app for the Conference on Ecological and Ecosystem Restoration. To access the conference app, scan the QR Code or search “IFAS OCI” in the App Store or Google Play on your Apple or Android device. Log in with the email address you used to register, a social media account, or as a guest. You will be prompted to select an event – choose CEER 2014. The event password is eco14. The app allows you to build a personal conference agenda, stay updated with conference announcements, and connect with sponsors, exhibitors, and fellow attendees. Should you have any questions about the app, please stop by our registration desk for assistance. Stay connected! #CEER2014 July 28-August 1, 2014 | New Orleans, LA USA Table of Contents Welcome Letter ...................................................................................................... 3 In Honor of David Allen Vigh ................................................................................... 4 About CEER ............................................................................................................. 6 About the Society for Ecological Restoration ........................................................
    [Show full text]
  • Self-Guided Naturalist Tour This Map and Attached Self-Guided Tour May Be Used for Free While at Earth Sanctuary
    Self-Guided Naturalist Tour This map and attached self-guided tour may be used for free while at Earth Sanctuary. If you would like to keep it, please deposit $1.00 in the Registration box. To take the self-guided naturalist tour, use this map in conjunction many acres of invasive species such as Himalayan blackberries with the 4x4 posts that have letters on top (e.g., A, B, etc.). Note: and replanted the with native vegetation. Over 15,000 individual the naturalist tour starts from the Newman Road Parking Lot. plants of over 80 species and over 3,000 trees have been planted to date in this effort. Window A – Parking lot by the trail to the Dolmen. Welcome Now let’s begin our exploration of Earth Sanctuary by to Earth Sanctuary. You are about to explore a beautiful jewel of heading down the trail to the Dolmen. We’re going to be looking a wooded wetland system that is home to many breeding and through a series of windows or snapshots into the processes of wintering ducks and waterfowl as well as many songbirds, frogs, life that are happening here. Look for Window B where the trail salamanders, beavers, muskrats, river otters, deer and other levels out beyond the bell. animals. It is such important habitat that it has been designated a “habitat of local importance” by Island County and by the Audubon Window B – A window into water and watersheds.. At this Society. Pause a moment to take a few deep breaths and be spot we are standing over the weir (water control structure present in spirit before you set out on your exploration.
    [Show full text]
  • Fens in a Large Landscape of West-Central Colorado
    Inventory of Fens in a Large Landscape of West-Central Colorado Grand Mesa, Uncompahgre, and Gunnison National Forests April 6, 2012 Beaver Skull Fen in the West Elk Mountains – a moat surrounding the floating mat Barry C. Johnstona, Benjamin T. Strattonb, Warren R. Youngc, Liane L. Mattsond, John M. Almye, Gay T. Austinf Grand Mesa, Uncompahgre, and Gunnison National Forests 2230 Highway 50, Delta, Colorado 81416-2485 a Botanist, Grand Mesa-Uncompahgre-Gunnison National Forests, Gunnison, CO. (970) 642-1177. [email protected] b Hydrologist, Grand Mesa-Uncompahgre-Gunnison National Forests, Gunnison, CO. (970) 642-4406. [email protected] cSoil Scientist, Grand Mesa-Uncompahgre-Gunnison National Forests, Montrose, CO. (970) 240-5411. [email protected] d Solid Leasable Minerals Geologist, USDA Forest Service Minerals and Geology Management, Centralized National Operation, Delta, CO. (970) 874-6697. [email protected] e Hydrologist (Retired), Grand Mesa-Uncompahgre-Gunnison National Forests, Delta, CO. f Resource Management Specialist, Bureau of Land Management, Gunnison, CO. (970-642-4943). [email protected]. 1 Acknowledgements Our deepest thanks go to Charlie Richmond, Forest Supervisor, for his support and guidance through this project; and to Sherry Hazelhurst, Deputy Forest Supervisor (and her predecessor, Kendall Clark), for valuable oversight and help over all the hurdles we have encountered so far. Carmine Lockwood, Renewable Resources Staff Officer, Lee Ann Loupe, External Communications Staff Officer, and Connie Clementson, Grand Valley District Ranger, members of our Steering Committee, gave much advice and guidance. Bill Piloni, Forest Fleet Manager, was most helpful with ironing out our vehicle situations. Doug Marah helped us get out some tight spots.
    [Show full text]
  • Botanical and Ecological Inventory of Peatland Sites on the Medicine Bow National Forest
    Botanical and Ecological Inventory of Peatland Sites on the Medicine Bow National Forest Prepared for Medicine Bow National Forest By Bonnie Heidel and Scott Laursen Wyoming Natural Diversity Database University of Wyoming P.O. Box 3381 Laramie, WY 82071 FS Agreement No. 02-CS-11021400-012 June 2003 ABSTRACT Peatlands are specialized wetland habitats that harbor high concentrations of Wyoming plant species of special concern. Intensive botanical and ecological inventories were conducted at five select peatland sites on Medicine Bow National Forest to further document the vascular flora, update information on plant species of special concern, initiate documentation of the bryophyte flora composition, and to document the vegetation associations. This provides a preliminary summary of peatland botanical and ecological resources on Medicine Bow National Forest, data for comparison between sites, and both floristic and vegetation plot datasets for comparison between Medicine Bow National Forest and Shoshone National Forest where parallel studies were undertaken. It might be used for more more extensive systematic inventories of peatlands and their associated botanical and ecological attributes across the Forest, or related efforts to evaluate watershed, wildlife, and other values associated with peatlands. ACKNOWLEDGEMENTS John Proctor (USFS Medicine Bow NF) contributed to fieldwork and provided Forest Service coordination that made this project a reality. Judy Harpel (USFS) made the moss species identifications for a segment of moss specimens, and provided encouragement in bryophyte research. George Jones (WYNDD) and Kathy Roche (USFS Medicine Bow NF) provided literature and comments on site selection and study aspects. Gary Beauvais provided administrative support. Chris Hiemstra and Mark Lyford (UW) provided study site data.
    [Show full text]
  • Wetland and Hydric Soils 6 Carl C
    Wetland and Hydric Soils 6 Carl C. Trettin, Randall K. Kolka, Anne S. Marsh, Sheel Bansal, Erik A. Lilleskov, Patrick Megonigal, Marla J. Stelk, Graeme Lockaby, David V. D’Amore, Richard A. MacKenzie, Brian Tangen, Rodney Chimner, and James Gries Introduction conterminous United States have been converted to other land uses over the past 150 years (Dahl 1990). Most of those losses Soil and the inherent biogeochemical processes in wetlands are due to draining and conversion to agriculture. States in the contrast starkly with those in upland forests and rangelands. The Midwest such as Iowa, Illinois, Missouri, Ohio, and Indiana differences stem from extended periods of anoxia, or the lack of have lost more than 85% of their original wetlands, and oxygen in the soil, that characterize wetland soils; in contrast, California has lost 96% of its wetlands. In the mid-1900s, the upland soils are nearly always oxic. As a result, wetland soil importance of wetlands in the landscape started to be under- biogeochemistry is characterized by anaerobic processes, and stood, and wetlands are now recognized for their inherent wetland vegetation exhibits specifc adaptations to grow under value that is realized through the myriad of ecosystem ser- these conditions. However, many wetlands may also have peri- vices, including storage of water to mitigate fooding, fltering ods during the year where the soils are unsaturated and aerated. water of pollutants and sediment, storing and sequestering car- This fuctuation between aerated and nonaerated soil condi- bon (C), providing critical habitat for wildlife, and recreation. tions, along with the specialized vegetation, gives rise to a wide Historically, drainage of wetlands for agricultural devel- variety of highly valued ecosystem services.
    [Show full text]