Washington Natural Heritage Program Presented to the Natural Heritage Advisory Council December 5, 2014
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Riparian Vegetation Management
Engineering in the Water Environment Good Practice Guide Riparian Vegetation Management Second edition, June 2009 Your comments SEPA is committed to ensuring its Good Practice Guides are useful and relevant to those carrying out activities in Scotland’s water environment. We welcome your comments on this Good Practice Guide so that we can improve future editions. A feedback form and details on how to send your comments to us can be found at the back of this guide in Appendix 1. Acknowledgements This document was produced in association with Northern Ecological Services (NES). Page 1 of 47 Engineering in the Water Environment Good Practice Guide: Riparian Vegetation Management Second edition, June 2009 (Document reference: WAT-SG-44) Contents 1 Introduction 3 1.1 What’s included in this Guide? 3 2 Importance of riparian vegetation 6 3 Establishing/creating vegetation 8 3.1 Soft or green engineering techniques 8 3.2 Seeding and planting of bare soil 10 3.3 Creating buffer strips 11 3.4 Planting trees and shrubs 15 3.5 Marginal vegetation 18 3.6 Urban watercourses 21 4 Managing vegetation 24 4.1 Management of grasses and herbs 24 4.2 Management of heath and bog 27 4.3 Management of adjacent wetlands 28 4.4 Management of non-native plant species 29 4.5 Management of scrub and hedgerows 31 4.6 Management of individual trees 31 4.7 Management of trees – riparian woodland 33 4.8 Management of trees – conifer plantations 35 4.9 Large woody debris 37 4.10 Marginal vegetation 37 4.11 Urban watercourses 40 4.12 Use of herbicides 40 4.13 Environmental management of vegetation 41 4.14 Vegetation management plans 41 5 Sources of further information 42 5.1 Publications 42 5.2 Websites 44 Appendix 1: Feedback form – Good Practice Guide WAT-SG-44 45 Page 2 of 47 1 Introduction This document is one of a series of good practice guides produced by SEPA to help people involved in the selection of sustainable engineering solutions that minimise harm to the water environment. -
A Unique Raised Bog at Urbana, Ohio.*
A UNIQUE RAISED BOG AT URBANA, OHIO.* ROBERT B. GORDON, Ohio State University. Located just north of the Champaign County Fair Grounds at Urbana, Ohio, is a unique dome-shaped bog, covered with shrubby vegetation for the most part, in which the center is raised at least ten feet above the margins. An old road crosses the bog. I have been told that it was once the main thorofare from Urbana to Columbus. Horses and wagons passed over it, I suppose, the drivers never realizing that a mat of fibrous roots less than one foot thick was all that held them over a body of water twelve feet in depth. Raised bogs, called "high moors" and "Hochmoore" in foreign literature, have long been known throughout Europe. N. S. Shaler is credited by Nichols with being the first to call attention to these peculiar swamps in North America, in 1888-89. Those which Shaler observed were "mostly limited to the eastern portion of Maine, near the shores of the Bay of Fundy," but some of lesser magnitude were reported for New Hampshire, northern Michigan, and Minnesota. Similar bogs, with centers about 13 feet above their margins, have been reported in the province of New Brunswick by Ganong (1897). Nichols (1919) described bogs of this type encountered in Maine, in which the elevation of the center above the margin varied from 2 or 3 feet to as high as 18 feet (e. g., Denbo Heath, covering several square miles in area). He asserts: "(1) that in the state of Maine raised bogs, in so far as they constitute a distinctive swamp type, are virtually restricted to the proximity of the seacoast; and (2) that in other portions of New England and of the eastern United States this type of bog is practically absent, although in occasional swamps it is possible to detect a slight elevation of the surface above the level of permanent ground water." Warming (1909) has summarized concisely the characteristic features of "Hochmoore." They owe their development to the growth of sphagnum mosses which absorb water that falls in the form of rain or snow. -
National Water Summary Wetland Resources: Maine
National Water Summary-Wetland Resources 213 Maine Wetland Resources M aine is rich in wetland resources. About 5 million acres, or one System Wetland description fourth of the State, is wetland. Maine has a wide variety of wetlands, Palustrine .................. Nontidal and tidal-freshwater wetlands in which ranging from immense inland peatlands to salt marshes and mud vegetation is predominantly trees (forested wet flats along the coast. lands); shrubs (scrub-shrub wetlands); persistent Wetlands are an integral part of Maine's natural resources. or nonpersistent emergent, erect, rooted herba ceous plants (persistent- and nonpersistent Wetlands provide essential habitat for certain types of wildlife and emergent wetlands); or submersed and (or) vegetation, including rare and endangered species. They are used floating plants (aquatic beds). Also, intermit for timber and peat; hunting, fishing, and shellfishing; education tently to permanently flooded open-water bod and research; and bird, wildlife and plant observation, all of which ies of less than 20 acres in which water is less than 6.6 feet deep. boost tourism and the general economy. Wetlands also provide flood control, bank and shoreline-erosion control, sediment retention, lacustrine ................. Nontidal and tidal-freshwater wetlands within an intermittently to permanently flooded lake or water fi ltration, and nutrient uptake. In recognition of the impor reservoir larger than 20 acres and (or) deeper tance of wetlands, many government and private organizations have than 6.6 feet. Vegetation, when present, is pre worked to preserve wetlands and educate the public about wetland dominantly nonpersistent emergent plants (non values. For example, the Maine Department of Conservation owns persistent-emergent wetlands), or submersed and (or) floating plants (aquatic beds), or both. -
This Document Was Withdrawn on 6 November 2017
2017. November 6 on understanding withdrawn was water for wildlife document This Water resources and conservation: the eco-hydrological requirements of habitats and species Assessing We are the Environment Agency. It’s our job to look after your 2017. environment and make it a better place – for you, and for future generations. Your environment is the air you breathe, the water you drink and the ground you walk on. Working with business, Government and society as a whole, we are makingNovember your environment cleaner and healthier. 6 The Environment Agency. Out there, makingon your environment a better place. withdrawn was Published by: Environment Agency Rio House Waterside Drive, Aztec West Almondsbury, Bristol BS32 4UD Tel: 0870document 8506506 Email: [email protected] www.environment-agency.gov.uk This© Environment Agency All rights reserved. This document may be reproduced with prior permission of the Environment Agency. April 2007 Contents Brief summary 1. Introduction 2017. 2. Species and habitats 2.2.1 Coastal and halophytic habitats 2.2.2 Freshwater habitats 2.2.3 Temperate heath, scrub and grasslands 2.2.4 Raised bogs, fens, mires, alluvial forests and bog woodland November 2.3.1 Invertebrates 6 2.3.2 Fish and amphibians 2.3.3 Mammals on 2.3.4 Plants 2.3.5 Birds 3. Hydro-ecological domains and hydrological regimes 4 Assessment methods withdrawn 5. Case studies was 6. References 7. Glossary of abbreviations document This Environment Agency in partnership with Natural England and Countryside Council for Wales Understanding water for wildlife Contents Brief summary The Restoring Sustainable Abstraction (RSA) Programme was set up by the Environment Agency in 1999 to identify and catalogue2017. -
Burns Bog Ecological Conservancy Area Management Plan May 2007
Burns Bog Ecological Conservancy Area Management Plan May 2007 BURNS BOG ECOLOGICAL CONSERVANCY AREA MANAGEMENT PLAN TABLE OF CONTENTS 1.0 INTRODUCTION................................................................................................... 1 1.1 Public Acquisition and Management of Lands........................................... 1 1.2 Planning Process....................................................................................... 2 2.0 BACKGROUND .................................................................................................... 3 2.1 Formation of Burns Bog............................................................................. 3 2.2 Significance of Burns Bog ......................................................................... 4 2.3 Cultural History .......................................................................................... 4 2.4 Recent Bog History.................................................................................... 5 3.0 MANAGEMENT CONTEXT .................................................................................. 5 4.0 THE BOG LANDS AND THE GVRD .................................................................... 7 5.0 VISION AND OBJECTIVES.................................................................................. 7 5.1 Vision – 100 Year Timeframe .................................................................... 7 5.2 Mission ...................................................................................................... 8 5.3 Management -
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. -
Assessment on Peatlands, Biodiversity and Climate Change: Main Report
Assessment on Peatlands, Biodiversity and Climate change Main Report Published By Global Environment Centre, Kuala Lumpur & Wetlands International, Wageningen First Published in Electronic Format in December 2007 This version first published in May 2008 Copyright © 2008 Global Environment Centre & Wetlands International Reproduction of material from the publication for educational and non-commercial purposes is authorized without prior permission from Global Environment Centre or Wetlands International, provided acknowledgement is provided. Reference Parish, F., Sirin, A., Charman, D., Joosten, H., Minayeva , T., Silvius, M. and Stringer, L. (Eds.) 2008. Assessment on Peatlands, Biodiversity and Climate Change: Main Report . Global Environment Centre, Kuala Lumpur and Wetlands International, Wageningen. Reviewer of Executive Summary Dicky Clymo Available from Global Environment Centre 2nd Floor Wisma Hing, 78 Jalan SS2/72, 47300 Petaling Jaya, Selangor, Malaysia. Tel: +603 7957 2007, Fax: +603 7957 7003. Web: www.gecnet.info ; www.peat-portal.net Email: [email protected] Wetlands International PO Box 471 AL, Wageningen 6700 The Netherlands Tel: +31 317 478861 Fax: +31 317 478850 Web: www.wetlands.org ; www.peatlands.ru ISBN 978-983-43751-0-2 Supported By United Nations Environment Programme/Global Environment Facility (UNEP/GEF) with assistance from the Asia Pacific Network for Global Change Research (APN) Design by Regina Cheah and Andrey Sirin Printed on Cyclus 100% Recycled Paper. Printing on recycled paper helps save our natural -
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. -
Lowland Raised Bog (UK BAP Priority Habitat Description)
UK Biodiversity Action Plan Priority Habitat Descriptions Lowland Raised Bog From: UK Biodiversity Action Plan; Priority Habitat Descriptions. BRIG (ed. Ant Maddock) 2008. This document is available from: http://jncc.defra.gov.uk/page-5706 For more information about the UK Biodiversity Action Plan (UK BAP) visit http://www.jncc.defra.gov.uk/page-5155 Please note: this document was uploaded in November 2016, and replaces an earlier version, in order to correct a broken web-link. No other changes have been made. The earlier version can be viewed and downloaded from The National Archives: http://webarchive.nationalarchives.gov.uk/20150302161254/http://jncc.defra.gov.uk/page- 5706 Lowland Raised Bog The definition of this habitat remains unchanged from the pre-existing Habitat Action Plan (https://webarchive.nationalarchives.gov.uk/20110303150026/http://www.ukbap.org.uk/UKPl ans.aspx?ID=20, a summary of which appears below. Lowland raised bogs are peatland ecosystems which develop primarily, but not exclusively, in lowland areas such as the head of estuaries, along river flood-plains and in topographic depressions. In such locations drainage may be impeded by a high groundwater table, or by low permeability substrata such as estuarine, glacial or lacustrine clays. The resultant waterlogging provides anaerobic conditions which slow down the decomposition of plant material which in turn leads to an accumulation of peat. Continued accrual of peat elevates the bog surface above regional groundwater levels to form a gently-curving dome from which the term ‘raised’ bog is derived. The thickness of the peat mantle varies considerably but can exceed 12m. -
Lowland Raised Bog, Duddon Mosses NNR, Cumbria
Lowland raised bog, Duddon Mosses NNR, Cumbria. © Natural England/Jacqueline Ogden 17. Lowland raised bog Climate Change Sensitivity: Medium Climate Change Adaptation Manual Evidence to support nature conservation in a changing climate 159 Introduction An intact, fully functioning lowland raised bog is expected to be relatively resilient to projected climate change, although both changes to patterns of rainfall, including extreme events and summer warming, will place increasing pressure on the habitat. In England, however, there are no raised bogs in this condition. The impact of historic and current land management has a significant impact on the vulnerability of sites. Damage through peat cutting or drainage (both on and off-site) that alters the hydrology of sites has significant adverse impacts on the ability of the bog to withstand reduced rainfall and extreme events such as drought. Degraded bogs are also more vulnerable to climate change impacts on the quality and quantity of ground water. In England, most remaining lowland raised bog habitat is found on the central or core area of the original dome. Surrounding this is an area of degraded peatland, often now under alternative land use, making the remaining bog increasingly vulnerable to off-site impacts and land-use change. Habitat Description Lowland raised bogs are peatland ecosystems which develop primarily in lowland areas such as at the head of estuaries, along river flood-plains and in topographic depressions. In such locations drainage has been impeded by a high groundwater table or by low permeability of the substrata. The resultant water-logging provides anaerobic conditions which slow down the decomposition of plant material, which in turn leads to an accumulation of peat. -
Peatlands (Mires) -All Peat Forming Habitats Eitherombrotrophic (Bogs, Moors, Muskegs) Orminerotrophic (Fens) - Extensively Studied, Especially in Northern Europe
Peatlands (mires) -all peat forming habitats eitherombrotrophic (bogs, moors, muskegs) orminerotrophic (fens) - extensively studied, especially in northern Europe - 2 to 3% of the terrestrial land surface, BUT 1/3 of global C pool !! 90% in arctic, boreal and temperate zones (Canada, Scandinavia, Russia) Tropical: Malasia Subalpine fen in the Tahoe Basin Tundra peatland Bog in the Tierra del Fuego Afro-alpine peatland 1 Type of peat deposit Pocosins – from Algonquin Indian word meaning “swamp -on- a-hill” - terrestrialization (“quaking bog”) - paludification (“blanket bog”) Terrestrialization Terrestrialization Aerial view of blanket bogs in Paludification(“blanket bog”) Scotland British Islands - for a long time paleoecologists thaught that blanket mires were climatically induced BUT - probably they have resulted from human activities ~ 3000 y BP cutting forest, reduced transpiration and interception 2 Aapa mires Classification patterned peatland; subarctic and boreal - S of permafrost line - according to water retention: ladderlike arrangement of long ridges (strings) alternating with wet depressions Primary (formed within water- (flarks ) perpendicular to the slope filled depressions or basins) dominant in N. Scandinavia, Labrador and Quebec the origin of strings and flarks is not very well understood ice pushing up the ridges in the pools peat sliding downslope Secondary (grow upward beyond the confines of the Aapa mire in Finland basin while still remaining under the influence of ground or surface water Tertiary (grow beyond the level of the groundwater source - perched above the accumulation of an impermeable peat) Palsa mires -zone of discontinuous permafrost on the southern edge of tundra Classification isolated mounds underlain by frozen peat and silt (permafrost) 5m tall, 150 m diam .