A Geographical Model for the Altitudinal Zonation of Mire Types in the Uplands of Western Europe: the Example of Les Monts Du Forez in Eastern France
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Annual Co and Ch Fluxes of Pristine Boreal Mires As a Background For
BOREAL ENVIRONMENT RESEARCH 12: 101–113 ISSN 1239-6095 Helsinki 11 May 2007 © 2007 Annual CO2 and CH4 fluxes of pristine boreal mires as a background for the lifecycle analyses of peat energy Sanna Saarnio1)*, Micaela Morero1), Narasinha J. Shurpali2), Eeva-Stiina Tuittila3), Markku Mäkilä4) and Jukka Alm5) 1) Faculty of Biosciences, University of Joensuu, P.O. Box 111, FI-80101 Joensuu, Finland (*corresponding author’s e-mail [email protected]) 2) Department of Environmental Sciences, University of Kuopio, P.O. Box 1627, FI-70211 Kuopio, Finland 3) Department of Forest Ecology, P.O. Box 27, FI-00014 University of Helsinki, Finland 4) Geological Survey of Finland, P.O. Box 96, FI-02151 Espoo, Finland 5) Finnish Forest Research Institute, Joensuu Research Unit, P.O. Box 68, FI-80101 Joensuu, Finland Received 18 Nov. 2005, accepted 24 Jan. 2007 (Editor in charge of this article: Raija Laiho) Saarnio, S., Morero, M., Shurpali, N. J., Tuittila, E.-S., Mäkilä, M. & Alm, J. 2007: Annual CO2 and CH4 fluxes of pristine boreal mires as a background for the lifecycle analyses of peat energy. Boreal Env. Res. 12: 101–113. This study was conducted to improve the estimates of C gas fluxes in boreal ombrotrophic and minerotrophic mires used in the lifecycle analysis of peat energy. We reviewed lit- erature and collected field data from two new sites in southern Finland. In the literature, –2 –1 annual estimates of net CO2 exchange varied from –85 to +67 g C m a for ombrotrophic –2 –1 mires and from –101 to +98 g C m a for minerotrophic mires. -
Vegetative Ecology of a Montane Mire, Crater Lake National
AJ ABSTRACT OF THE THESIS OF Susan Cornelia Seyer for the degree of Master of Science in Botany and Plant Pathology presented on December 14, 1979 Title: VEGETATIVE ECOLOGY OF A MONTANE MIRE, CRATER LAKE NATIONAL PARK, OREGON Redacted for Privacy Abstract approved: Jerry F. Franklin Mires, or peat-producing ecosystems, dominated by sedges, shrubs, and brown mosses, are common features in Cascade subalpine regions, occurring where moisture accumulates in small basins or on poorly-drained slopes. Although descriptions and classifications have been developed for mire vegetation in much of the world, there is little information of even a descriptive nature for these montane mires in Oregon and Washington. This thesis reports on phytosocia- logical structure, env'ironental relations, and successional trends in one such mire in the Oregon Cascade mountains. To characterize the general phytosociological structure of the mire vegetation at Sphagnum Bog, Crater Lake National Park, quantitative species cover data were used in conjunction with a Braun-Blanquet tabular analysis and two-dimensional stand ordinations, reciprocal averaging and a Bray-Curtis polar ordination. Defined community types correspond to physiognomic types as follows: Carex rostrata (reedswamp); Eleocharis pauciflora-Carex limosa, Eleocharis pauciflora/bryophytes (low sedge fens); Carex sichensis (tall sedge fen); Vaccinium/ Aulacomnium palustre, Vaccinium occidentala/Carex sitchensis (shrub thickets; Alnus incana/Brachythacium sp. and Salix barclayi (marginal carrs).Phases were defined when appropriate. A vegetation map was made to illustrate the locations and extent of the variouscommunities. Comparisons with other montane mires in thearea determined that the physiognomic units defined are repeatable when appropriate habitat conditions are present, and that they usually includemany of the same characteristic species, the dominant mosses being particularly constant. -
Rich Conifer Swamp Communityrich Conifer Abstract Swamp, Page 1
Rich Conifer Swamp CommunityRich Conifer Abstract Swamp, Page 1 Community Range Photo by Michael R. Penskar Prevalent or likely prevalent Infrequent or likely infrequent Absent or likely absent Overview: Rich conifer swamp is a groundwater- communities are minerotrophic wetlands but differ in influenced, or minerotrophic, forested wetland that is species composition because of the absence of northern dominated by northern white cedar (Thuja occidentalis) white cedar, which often forms a dense canopy. An- and occurs on organic soils (e.g., peat and muck). The other type of conifer-dominated wetland, poor conifer community is often referred to as cedar swamp. swamp, which occurs primarily in northern Michigan, can be distinguished from rich conifer swamp by its Global and State Rank: G4/S3 acidic organic soils, lack of groundwater influence (i.e., ombrotrophic), and prevalence of black spruce (Picea Range: Rich conifer swamp occurs throughout the up- mariana) and/or tamarack (Kost et al. 2007). Stands of per Midwest and northeast United States and adjacent mixed conifers and hardwoods that occur on saturated Canadian provinces (Faber-Langendoen 2001, Nature- mineral or muck soils are classified as hardwood- Serve 2001). The community varies in overall species conifer swamp and also occur primarily in northern composition across its range, which includes Michigan, Michigan (Kost et al. 2007). Boreal forest, which is Minnesota, Wisconsin, Ontario, Manitoba, Quebec, often dominated by northern white cedar, is sometimes New York, New Hampshire, Vermont, Maine, and confused with rich conifer swamp. Unlike rich conifer northern Illinois, Indiana and Ohio (Faber-Langendoen swamp, most boreal forests in Michigan are upland 2001, NatureServe 2001). -
Taiga Plains
ECOLOGICAL REGIONS OF THE NORTHWEST TERRITORIES Taiga Plains Ecosystem Classification Group Department of Environment and Natural Resources Government of the Northwest Territories Revised 2009 ECOLOGICAL REGIONS OF THE NORTHWEST TERRITORIES TAIGA PLAINS This report may be cited as: Ecosystem Classification Group. 2007 (rev. 2009). Ecological Regions of the Northwest Territories – Taiga Plains. Department of Environment and Natural Resources, Government of the Northwest Territories, Yellowknife, NT, Canada. viii + 173 pp. + folded insert map. ISBN 0-7708-0161-7 Web Site: http://www.enr.gov.nt.ca/index.html For more information contact: Department of Environment and Natural Resources P.O. Box 1320 Yellowknife, NT X1A 2L9 Phone: (867) 920-8064 Fax: (867) 873-0293 About the cover: The small photographs in the inset boxes are enlarged with captions on pages 22 (Taiga Plains High Subarctic (HS) Ecoregion), 52 (Taiga Plains Low Subarctic (LS) Ecoregion), 82 (Taiga Plains High Boreal (HB) Ecoregion), and 96 (Taiga Plains Mid-Boreal (MB) Ecoregion). Aerial photographs: Dave Downing (Timberline Natural Resource Group). Ground photographs and photograph of cloudberry: Bob Decker (Government of the Northwest Territories). Other plant photographs: Christian Bucher. Members of the Ecosystem Classification Group Dave Downing Ecologist, Timberline Natural Resource Group, Edmonton, Alberta. Bob Decker Forest Ecologist, Forest Management Division, Department of Environment and Natural Resources, Government of the Northwest Territories, Hay River, Northwest Territories. Bas Oosenbrug Habitat Conservation Biologist, Wildlife Division, Department of Environment and Natural Resources, Government of the Northwest Territories, Yellowknife, Northwest Territories. Charles Tarnocai Research Scientist, Agriculture and Agri-Food Canada, Ottawa, Ontario. Tom Chowns Environmental Consultant, Powassan, Ontario. Chris Hampel Geographic Information System Specialist/Resource Analyst, Timberline Natural Resource Group, Edmonton, Alberta. -
Changes in Peat Chemistry Associated with Permafrost Thaw Increase Greenhouse Gas Production
Changes in peat chemistry associated with permafrost thaw increase greenhouse gas production Suzanne B. Hodgkinsa,1, Malak M. Tfailya, Carmody K. McCalleyb, Tyler A. Loganc, Patrick M. Crilld, Scott R. Saleskab, Virginia I. Riche, and Jeffrey P. Chantona,1 aDepartment of Earth, Ocean, and Atmospheric Science, Florida State University, Tallahassee, FL 32306; bDepartment of Ecology and Evolutionary Biology, University of Arizona, Tucson, AZ 85721; cAbisko Scientific Research Station, Swedish Polar Research Secretariat, SE-981 07 Abisko, Sweden; dDepartment of Geological Sciences, Stockholm University, SE-106 91 Stockholm, Sweden; and eDepartment of Soil, Water and Environmental Science, University of Arizona, Tucson, AZ 85721 Edited by Nigel Roulet, McGill University, Montreal, Canada, and accepted by the Editorial Board March 7, 2014 (received for review August 1, 2013) 13 Carbon release due to permafrost thaw represents a potentially during CH4 production (10–12, 16, 17), δ CCH4 also depends on 13 major positive climate change feedback. The magnitude of carbon δ CCO2,soweusethemorerobustparameterαC (10) to repre- loss and the proportion lost as methane (CH4) vs. carbon dioxide sent the isotopic separation between CH4 and CO2.Despitethe ’ (CO2) depend on factors including temperature, mobilization of two production pathways stoichiometric equivalence (17), they previously frozen carbon, hydrology, and changes in organic mat- are governed by different environmental controls (18). Dis- ter chemistry associated with environmental responses to thaw. tinguishing these controls and further mapping them is therefore While the first three of these effects are relatively well under- essential for predicting future changes in CH4 formation under stood, the effect of organic matter chemistry remains largely un- changing environmental conditions. -
Modeling the Boundaries of Plant Ecotones of Mountain Ecosystems
Article Modeling the Boundaries of Plant Ecotones of Mountain Ecosystems Yulia Ivanova 1,* and Vlad Soukhovolsky 2 1 Institute of Biophysics, Siberian Branch, Russian Academy of Sciences, Federal Research Center “Krasnoyarsk Science Center SB RAS”, Academgorodok 50-50, 600036 Krasnoyarsk, Russia 2 V.N. Sukachev Institute of Forest, Siberian Branch, Russian Academy of Sciences, Federal Research Center “Krasnoyarsk Science Center SB RAS”, Academgorodok 50-28, 600036 Krasnoyarsk, Russia; [email protected] * Correspondence: [email protected]; Tel.: +7-391-249-4328; Fax: +7-391-243-3400 Academic Editors: Isabel Cañellas and Timothy A. Martin Received: 30 August 2016; Accepted: 5 November 2016; Published: 12 November 2016 Abstract: The ecological second-order phase transition model has been used to describe height-dependent changes in the species composition of mountain forest ecosystems. Forest inventory data on the distribution of various tree species in the Sayan Mountains (south Middle Siberia) are in good agreement with the model proposed in this study. The model was used to estimate critical heights for different altitudinal belts of vegetation, determine the boundaries and extents of ecotones between different vegetation belts, and reveal differences in the ecotone boundaries between the north- and south-facing transects. An additional model is proposed to describe ecotone boundary shifts caused by climate change. Keywords: ecotone; boundaries of ecotones; mountain forest ecosystems; biodiversity 1. Introduction Any plant community has its own species composition and spatial structure. Within the space occupied by the community, it may be regarded as uniform and characterized by spatially invariable parameters. The boundaries of a community are determined by the effects of external modifying factors (such as temperature) on the plants and competitive interactions between the species that are not characteristic of this community but are present in the neighboring one [1,2]. -
The Structure and Composition of Vegetation in the Lake-Fill Peatlands of Indiana
2001. Proceedings of the Indiana Academy of Science 1 10:51-78 THE STRUCTURE AND COMPOSITION OF VEGETATION IN THE LAKE-FILL PEATLANDS OF INDIANA Anthony L. Swinehart 1 and George R. Parker: Department of Forestry and Natural Resources, Purdue University, West Lafayette, Indiana 47907 Daniel E. Wujek: Department of Biology, Central Michigan University, Mount Pleasant, Michigan 48859 ABSTRACT. The vegetation of 16 lake-fill peatlands in northern Indiana was systematically sampled. Peatland types included fens, tall shrub bogs, leatherleaf bogs and forested peatlands. No significant difference in species richness among the four peatland types was identified from the systematic sampling. Vegetation composition and structure, along with water chemistry variables, was analyzed using multi- variate statistical analysis. Alkalinity and woody plant cover accounted for much of the variability in the herbaceous and ground layers of the peatlands, and a successional gradient separating the peatlands was evident. A multivariate statistical comparison of leatherleaf bogs from Indiana, Michigan, Ohio, New York, New Jersey and New Hampshire was made on the basis of vegetation composition and frequency and five climatic variables. The vascular vegetation communities of Indiana peatlands and other peatlands in the southern Great Lakes region are distinct from those in the northeastern U.S., Ohio and the northern Great Lakes. Some of these distinctions are attributed to climatic factors, while others are related to biogeo- graphic history of the respective regions. Keywords: Peatlands, leatherleaf bogs, fens, ecological succession, phytogeography Within midwestern North America, the such as Chamaedaphne calyculata, Androm- northern counties of Illinois, Indiana and Ohio eda glaucophylla, and Carex oligospermia of- 1 represent the southern extent of peatland com- ten make "southern outlier peatlands ' con- munities containing characteristic plant spe- spicuous to botanists, studies of such cies of northern or boreal affinity. -
Does Soil Fertility Influence the Vegetation Diversity of a Tropical Peat Swamp
Does soil fertility influence the vegetation diversity of a tropical peat swamp forest in Central Kalimantan, Indonesia? By Leanne Elizabeth Milner Dissertation presented for the Honours degree of BSc Geography Department of Geography University of Leicester 24 th February 2009 Approx number of words (12,000) 1 Contents Page LIST OF FIGURES I LIST OF TABLES II ABSTRACT III ACKNOWLEGEMENTS IV Chapter 1: Introduction 1 1.1 Aim 2 1.2 Objectives 2 1.3 Hypotheses 2 1.4 Scientific Background and Justification 3 1.5 Literature Review 7 1.5.1 Soil Fertility and Vegetation Species Diversity 7 1.5.2 Tropical Peatlands 7 1.5.3 Vegetation and Soil in tropical peatlands 8 1.5.4 Hydrology 14 1.5.5 Phenology and Rainfall 15 Chapter 2 : Methodology 17 2.1 Study Site and Transects 18 2.2 Soil Analysis 21 2.3 Chemical Analysis 22 2.4 Tree Data 25 2.5 Phenology Data 25 2.6 Rainfall Data 26 2.7 Data Analysis 26 2.7.1 Soil Data Analysis 26 2.7.2 Tree Data Analysis 26 2.7.3 Phenology Data Analysis 28 2 2.7.4 Rainfall Data Analysis 28 Chapter 3: Analysis 29 3.1 Tree and Liana Analysis 30 3.1.1 Basal Area and Density 31 3.1.2 Relative Importance Values 33 3.2 Peat Chemistry Analysis 35 3.3 Tree Phenology Analysis 43 3.4 Rainfall Analysis 46 Chapter 4: Discussion 47 4.1 Overall Findings 48 4.2 Peat Chemistry 48 4.3 Vegetation and Phenology 51 4.4 Peat Depth and Gradient 53 4.5 Significance of the Water Table 54 4.6 Limitations and Areas for further Research 56 Chapter 5: Conclusion 59 5.0 Conclusion 60 REFERENCES 62 APPENDICES 67 Appendix A: Soil Nutrient Analysis 68 Appendix B: Regression Outputs 70 Appendix C: Tree Data ON CD Appendix D: Phenology Data ON CD 3 List of Figures Figure 1 – Distribution of tropical peatlands in South East Asia and location of the study area. -
CHEMICAL and PHYSICAL CHARACTERISTICS of SHALLOW GROUND WATERS in NORTHERN MICHIGAN BOGS, SWAMPS, and Fensl
Amer. J. Bot. 69(8): 1231-1239. 1982. CHEMICAL AND PHYSICAL CHARACTERISTICS OF SHALLOW GROUND WATERS IN NORTHERN MICHIGAN BOGS, SWAMPS, AND FENSl 2 4 CHRISTA R. SCHWINTZER ,3 AND THOMAS J. TOMBERLIN The University of Michigan Biological Station," Pellston, Michigan 49769, Harvard University, Harvard Forest, Petersham, Massachusetts 01366, and Department of Statistics! Harvard University, Cambridge, Massachusetts 02138 ABSTRACT Fifteen chemical and physical characteristics were examined in samples of shallow ground water taken in midsummerat 15-30em below the surface in six bogs, 15 swamps, and six fens. The wetland types were identified on the basis of their vegetation. Three groups of covarying water characteristics were identified by factor analysis. Factor I included Ca, Mg, Si, pH, alkalinity, conductivity and to a much lesser extent Na, and reflects the degree of telluric water influence in the wetland. Factor 2 included reactive-P, total-P, NH,,-N, and to a lesser extent K, and consists of elements that primarily enter interstitial water via organic matter decom position. Factor 3 included Na, Cl, and to a much lesser extent K. The wetlands formed two distinct groups with respect to water chemistry: weakly minero trophic (pH 3.8-4.3) including all bogs and moderately to strongly minerotrophic (pH 5.5-7.4) includingall swamps and fens. The bogs had very low values for Factor 1 characteristics and moderate values for the remaining characteristics. The swamps and fens had moderate to high values for Factor I characteristics and showed considerable overlap in this respect. The fens had consistently low values for Factor 2 characteristics but overlapped with some swamps which also had low Factor 2 scores. -
D3.1 Palsa Mire
European Red List of Habitats - Mires Habitat Group D3.1 Palsa mire Summary Palsa mire develops where thick peat is subject to sporadic permafrost in Iceland, northern Fennoscandia and arctic Russia where there is low precipitation and an annual mean temperature below -1oC. The permafrost dynamics produce a typical patterning with palsa mounds 2-4m (sometimes 7m) high elevated in central thicker areas by permafrost lenses, the carpet of Sphagnum peat limiting the penetration of thaw, and a perennially frozen core of peat, silt and ice lenses beneath. Pounikko hummock ridges can be found in marginal areas subject to seasonal freezing and there are plateau-wide palsas and pounu string mires in the arctic. Intact palsa mounds show a patterning of weakly minerotrophic vegetation with different assemblages of mosses, herbs and sub-shrubs on their tops and sides. Old palsa mounds can become dry and erosion may lead to melting and collapse. Complete melting leaves behind thermokarst ponds. Palsa mires have experienced substantial decline and deterioration in recent years and, although these changes are not yet dramatic, all estimations indicate high probability of collapse as a result of climatic warming. Climate change mitigation measures are decisive to prevent the collapse of this habitat type. Synthesis This habitat type is assessed as Critically Endangered (CR) under Criterion E as its probability of collapse within the next 50 years is estimated to be over 50% as a result of climate warming. This quantitative analysis has been performed by reviewing and analyzing published research articles, together with unpublished contributions from experts, by including probabilistic modeling of future trends and linear extrapolation of recent trends to support model predictions. -
2.2 Ecosystems of the World E
Ecotoxicology and Climate Edited by P. Bourdeau, J. A. Haines, W. Klein and C. R. Krishna Murti @ 1989 SCOPE. Published by John Wiley & Sons Ltd 2.2 Ecosystems of the World E. F. BRUENIG 2.2.1 DEFINITION An ecosystem is a community of organisms and their physical and chemical environment interacting as an ecological unit. It represents all biological and abiotic components, including man, within a defined and delimited biotope, and is characterized by distinct ecological biocoenotic features of structure and functioning. The ecosystem relates to many different scales. At the lowest end of the scale, the ecosystem may comprise a rock, a fallen tree, or a certain layer in a plant community (pico-ecosystem, as described by Ellenberg, 1973). At the largest end of the scale it relates to life support media and covers oceanic, terrestrial, limnic, or urban ecosystem categories (mega-ecosystem). The present description is restricted to terrestrial ecosystems and focuses in particular on potential natural vegetation. Centred on the plant formation, it classes natural forests and woodlands in hot and cold climates at macro-ecosystem level. The description is structured by classifying the forests and woodlands at micro- ecosystem (formation group) level according to major physiognomic, pheno- logical, and growth features in relation to the site and environmental conditions. These units correspond roughly to the bioclimatic life zones of Holdridge (1967). The description is patterned on the serial structure of the physiognomic- ecological classification of plant formations of the earth (Miiller-Dombois and Ellenberg, 1974, pp. 466-488) commonly quoted as the UNESCO Classification. 2.2.2 NATURAL VEGETATIONAL ZONES 2.2.2.1 Latitudinal Zonation The characteristic features of the zonal vegetation in each latitudinal zone are primarily determined and shaped by climate. -
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.