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MANAGEMENT of the MARSHES
MANAGEMENT of the MARSHES An analysis of the intentions of farmers and landowners in respect of marsh management post ESA and Environmental Stewardship. Strumpshaw Fen, RSPB Produced by Farm Conservation. Funded by the Broads Authority and the Norfolk Biodiversity Partnership. October 2014 MANAGEMENT of the MARSHES The report is a Broads Authority and Norfolk Biodiversity Partnership initiative, undertaken by Farm Conservation Limited, supported by Broads Authority for mapping, and working with Natural England. Project manager Andrea Kelly, Senior Ecologist (Broads Authority) Anne Casey, Coordinator Norfolk Biodiversity Partnership Acknowledgements: ;OHURZHYLK\L[V[OLTHU`MHYTLYZHUKSHUKV^ULYZ^OV[VVR[OL[YV\ISL[VÄSSPUVUSPULVYWHWLY X\LZ[PVUUHPYLZ4HU`V[OLYMHYTLYZ[OLUHSZV[VVRWHY[PU[LSLWOVULX\LZ[PVUUHPYLZVYMHJL[VMHJLPU[LY]PL^Z ;OHURZHSZVNV[VZL]LYHS-HYT(K]PZLYZ^OVNH]L[OLPYHK]PJLHUK[OLILULÄ[VM[OLPYL_WLYPLUJLMYLLS`HUK generously, particularly Robert Camps and Richard MacMullen. Thanks also to Andrea Kelly, Broads Authority and Mike Edwards, Natural England for assisting with design of the questionaire and scoping the project, to Norfolk Biodiversity Partnership who funded the work, and to Sam Neal at NBIS who provided some of the data. We also acknowledge the contribution made by the Communications Team at Anglia Farmers, particularly :HT)HYYLSSHUK7H\S)HSL^OVOLSWLKKL]LSVW[OLVUSPULX\LZ[PVUUHPYLHUKMVY[OLÄUHSWYVK\J[PVU of the report. Citation: Authors: Gelpke S, Thompson H, and Walker H, (29th October 2014) Management of the Marshes. Broads Authority -
Design & Reporting Criteria for Reed Bed & Fen
DESIGN AND REPORTING CRITERIA FOR REED BED AND FEN RESTORATION IN MINERAL WORKINGS 1 R Neil Humphries and Roger Meade 2 Abstract. Hanson Quarry Products Europe and the statutory nature conservation body for England, English Nature (now Natural England), have a Partnership Agreement whereby Hanson in 2002 became the UK Habitats Champion for reed bed and fen recovery. Both reed bed and fen habitats are identified as a priority to halt their recent decline and to be enhanced and expanded in the UK Biodiversity Action Plan (BAP). The mineral extraction industry can significantly contribute to the 2010 national recovery targets. In 2003 English Nature commissioned, and subsequently published in 2007, 'Design & Reporting Criteria' to guide and facilitate the successful creation of reed bed, other swamp and fen vegetation as an after use of mineral extraction sites, and their subsequent reporting for inclusion in the national UK and local Habitat BAP inventories and audits. Reed bed is a specific type of open-water transition fen dominated by the common reed Phragmites australis and fen a generic term for this and other wetland types influenced by water that has been in contact with rock or soil. The term 'fen' embraces a very wide range of vegetation composition from low sedge and moss dominated to tall reed and tall-herb swamp types, and grading into the ‘wet’ end of meadows and woodland types. The scope for the creation of the various types of fen is dependent on a number of key physical factors (climate, hydrology, substrate (soils and geology) and fertility), but also in practice, land management and the availability of plant material. -
The Reed Bed System
Constructed Wetland Group Reed Bed Systems for Biosolids Treatment An Innovative and Cost Effective Approach to Wastewater and Sludge Treatment Constructed Wetlands Group, Inc. Aiken, MN Maiden Creek, PA Reed BedsAliquippa, PA in OperationMarion, WI Amity Township, PA Marlboro Developmental Ctr., Marlboro, NJ Ancora State Hospital, Ancora, NJ Morysville, PA Appomattox, VA Myerstown, PA Belgium, WI Mercersburg, PA Bethel, ME New Jersey School Of Conservation, Beverly, NJ Branchville, NJ Birdsboro, PA New Paris, IN Blairsville, PA Northern Lancaster County Authority, Bowmanstown, PA Denver, PA Brillion, WI North Warren, PA Burgettstown, PA Oley, PA Caribou, ME Oneida Tribe of Wisconsin Central Carbon, PA Orbissonia Rockhill , PA Culver, IN Orwigsburg, PA Deer Lake, PA Penn Yan, NY Delano, MN Pine River, MN Denton, MD Red Cliff Band of Chippewa, WI Elizabethville, PA Robeson, PA Falls City, NE Robesonia Wernersville, PA Fleetwood, PA Royersford, PA Friendship, NY Saint Michael, MN Greencastle, IN Salem, MO Green Lane, PA Schuylkill County MUA, Gordon, PA Harrison Township, PA Shade Gap, PA Hawley Area Authority, PA Sherwood, WI Indian Head, MD Shickshinny, PA Kasson, MN Sinking Spring, PA Kewaunee, WI Slatington, PA Kirklin, IN South Middleton, PA Kla-Mo-Ya Tribe, Chiloquin, OR Susquehanna, PA Kouts, IN Union Township (Belleville), PA Kingsford Heights, IN U.S. Parks Service, Sandy Hook, NJ Kutztown, PA Wanatah, IN Linton, IN Washburn, WI Lehigh Township, PA Washington Township, NJ Lomira, WI West Monmouth MUA, NJ Lowell, IN Winter Harbor, ME Lyons Township, PA Woodbine, NJ Mabel, MN Womelsdorf, PA Mahanoy City, PA On-Site Water and Wastewater Treatment An effective, cost-saving approach to dewatering sludge www.reedbed.com Email:[email protected] History of Reed Beds . -
Removal of Salinity Using Interaction Mangrove Plants and Bacteria in Batch Reed Bed System Reactor
Journal of Ecological Engineering Received: 2018.10.30 Revised: 2018.12.01 Volume 20, Issue 4, April 2019, pages 84–93 Accepted: 2019.02.16 Available online: 2019.02.27 https://doi.org/10.12911/22998993/102792 Removal of Salinity using Interaction Mangrove Plants and Bacteria in Batch Reed Bed System Reactor Rachmi Layina Chimayati1*, Harmin Sulistiyaning Titah1 1 Department of Environmental Engineering, Faculty of Civil, Environmental and Geo Engineering, Institut Teknologi Sepuluh Nopember, Keputih, Sukolilo, 60111 Surabaya, Indonesia * Corresponding author’s e-mail: [email protected] ABSTRACT The current method of seawater bio-desalination can effectively provide freshwater. This method works by sepa- rating the salt contained in water into clean water with a lower salinity. In this study, the researchers conducted an experiment of the bio-desalination method by combining mangrove plant and Vibrio alginolyticus bacteria as well as the presence of a filter layer component composed of sand and gravel in red beed system reactor. The concept of phytotechnology was to utilize plants as environmental technology capable of solving environmental problems. In contrast, the term phytoremediation was used to denote the process of plants absorb, take, change and release con- taminants from one medium to another. The purpose of this study was to determine the reduction of salinity on the mangrove plant Rhizophora mucronata (Rm) and Avicennia marina (Am) with the addition of Vibrio alginolyticus (Va) bacteria in the bio-desalination process using a reed bed system. This study combines plants and bacteria for artificial saline desalination processes. The compounds contained in plants are absorbed in the form of cations or anions, while the addition of the bacteria was carried out to support the process of salt absorption in plants. -
Diversity, Current Knowledge and the Significance of the Flora of Tasek Bera Ramsar Site, Pahang, Malaysia
Journal of Wildlife and Parks (2014) 27 : 111-120 111 DIVERSITY, CURRENT KNOWLEDGE AND THE SIGNIFICANCE OF THE FLORA OF TASEK BERA RAMSAR SITE, PAHANG, MALAYSIA Rafidah, A.R.*, Chew, M.Y., Ummul-Nazrah, A.R. & Kamarudin, S. Flora Biodiversity Program, Forest Biodiversity Division, Forest Research Institute Malaysia (FRIM) *Corresponding author: [email protected] ABSTRACT Tasek Bera — the largest natural freshwater lake in Peninsular Malaysia is made up of a mosaic of micro-habitats and flora communities, including open water, rassau swamp, Lepironia reed-bed, seasonal freshwater swamp forest and the surrounding lowland dipterocarp forest. Botanical collecting and transect studies on the various habitats were carried out in 2007 to 2009, the last was part of the Biodiversity Inventory of Ramsar Site, in both the wet and dry seasons. The aquatic or swampy habitats covered were Lubuk Gah Bahau, Lubuk Hantu Tinggi, Lubuk Kuin, Lubuk Luon, Lubuk Pa Arit, Lubuk Ranting Patah, Lubuk Regeh, Lubuk Sangla Besar, Lubuk Sangla Kecil, Sungai Bera and Sungai Tasik; while forested habitats surveyed were Batin Md. Nor (Penchok) Camp, FELDA Bera 3 and 5, Kampung Gegereh, Kampung Jelawat, Kampung Pathir, Mekok Camp, Pos Iskandar, Pulau Jelai, Taman Herba and Tanjung Kuin. Previous surveys had recorded 52 species of vascular plants from the open water, rassau swamp and lowland dipterocarp forest habitats visited, representing a mere 6% of the total 807 species from 400 genera and 128 families, now known to occur in Tasek Bera. Satellite imagery records that 67% of Tasek Bera consists of freshwater swamp forest. However, this habitat type is still the least known despite numerous field surveys, due to logistic difficulties in accessing these boggy swamps sandwiched between tall rassau thickets and lowland dipterocarp forest. -
Proposed Residential Development, Land Off Barrowby Road, Grantham Lincolnshire
GLADMAN DEVELOPMENTS LTD PROPOSED RESIDENTIAL DEVELOPMENT, LAND OFF BARROWBY ROAD, GRANTHAM LINCOLNSHIRE Environmental Impact Assessment Environmental Statement December 2014 14268-R02 v3 ES COPYRIGHT The copyright of this document remains with Aspect Landscape Planning Ltd. The contents of this document therefore must not be copied or reproduced in whole or in part for any purpose without the written consent of Aspect Landscape Planning Ltd. Aspect Landscape Planning Ltd Hardwick Business Park Noral Way Banbury Oxfordshire OX16 2AF t 01295 276066 f 01295 265072 e [email protected] w www.aspect-landscape.com CONTENTS INTRODUCTION ............................................................................................................... 3 CONTEXT................................................................................................................................................. 3 OVERVIEW .............................................................................................................................................. 3 THE PROJECT TEAM ................................................................................................................................... 5 ENVIRONMENTAL IMPACT ASSESSMENT METHODOLOGY ............................................... 8 INTRODUCTION ........................................................................................................................................ 8 ENVIRONMENTAL IMPACT ASSESSMENT REGULATIONS .................................................................................... -
A Manual for the Survey and Evaluation of the Aquatic Plant and Invertebrate Assemblages of Grazing Marsh Ditch Systems
A manual for the survey and evaluation of the aquatic plant and invertebrate assemblages of grazing marsh ditch systems Version 6 Margaret Palmer Martin Drake Nick Stewart May 2013 Contents Page Summary 3 1. Introduction 4 2. A standard method for the field survey of ditch flora 5 2.1 Field survey procedure 5 2.2 Access and licenses 6 2.3 Guidance for completing the recording form 6 Field recording form for ditch vegetation survey 10 3. A standard method for the field survey of aquatic macro- invertebrates in ditches 12 3.1 Number of ditches to be surveyed 12 3.2 Timing of survey 12 3.3 Access and licences 12 3.4 Equipment 13 3.5 Sampling procedure 13 3.6 Taxonomic groups to be recorded 15 3.7 Recording in the field 17 3.8 Laboratory procedure 17 Field recording form for ditch invertebrate survey 18 4. A system for the evaluation and ranking of the aquatic plant and macro-invertebrate assemblages of grazing marsh ditches 19 4.1 Background 19 4.2 Species check lists 19 4.3 Salinity tolerance 20 4.4 Species conservation status categories 21 4.5 The scoring system 23 4.6 Applying the scoring system 26 4.7 Testing the scoring system 28 4.8 Conclusion 30 Table 1 Check list and scoring system for target native aquatic plants of ditches in England and Wales 31 Table 2 Check list and scoring system for target native aquatic invertebrates of grazing marsh ditches in England and Wales 40 Table 3 Some common plants of ditch banks that indicate salinity 50 Table 4 Aquatic vascular plants used as indicators of good habitat quality 51 Table 5a Introduced aquatic vascular plants 53 Table 5a Introduced aquatic invertebrates 54 Figure 1 Map of Environment Agency regions 55 5. -
Natural and Economic Factors of Shrinkage of Lakes of the Wielkopolska Lakeland
Limnological ReviewNatural (2011)and economic 11, 3: 123-132 factors of shrinkage of lakes of the Wielkopolska Lakeland 123 DOI 10.2478/v10194-011-0034-0 Natural and economic factors of shrinkage of lakes of the Wielkopolska Lakeland Bogumił Nowak1, Barbara Brodzińska2, Izabela Gezella-Nowak 1 Adam Mickiewicz University in Poznań, Institute of Geology, Maków Polnych 16, 61-606 Poznań, Poland; e-mail: [email protected] 2 Institute of Meteorology and Water Management – National Research Institute, Poznań Branch, Dąbrowskiego 174/176, 60-594 Poznań, Poland; e-mail: [email protected] Abstract: The paper discusses the issue of plant overgrowth in the littoral zone of lakes. It presents the plant encroachment process and its environmental and economic consequences based on the example of selected lakes of the Wielkopolska Lakeland. In order to estimate changes of quantity in the riparian vegetation structure, historical records of changes of reed bed areas were compared with their present areas. Historical data included bathymetric plans from the 1960’s created by the Institute of Inland Fisheries and information obtained from interviews with the inhabitants of settlements located in the vicinity of the studied lakes. Present-day boundaries of reed bed zones were identified using orthophotos, aerial photographs and in situ inspections. In the course of the field research, identification of plant species and estimates of plant condition in the studied stands were carried out. Obtained data combined with data on local hydrological-meteorological conditions, water quality and land use in the direct vicinity of lakes allowed the authors to determine the conditioning factors of riparian vegetation encroachment. -
Reed Beds for the Treatment of Tannery Effluent
UNITED NATIONS INDUSTRIAL DEVELOPMENT ORGANIZATION September 2001 US/RAS/92/120 Regional Programme for pollution control in the tanning industry in South-East Asia REED BEDS FOR THE TREATMENT OF TANNERY EFFLUENT Prepared by K.V. Emmanuel National Expert-Environmental Engineering Project Manager Jakov Buljan Agro-industries and Sectoral Support Branch This paper has not been edited The views presented are those of the authors and are not necessarily shared by UNIDO References herein to any specific commercial product, process, or manufacturer do not necessarily constitute or imply its endorsement or recommendation by UNIDO TABLE OF CONTENTS LIST OF SYMBOLS & ABBREVIATIONS ...................................................................... iii EXECUTIVE SUMMARY .................................................................................................... iv 1. BACKGROUND .................................................................................................................. 1 2. OBJECTIVES ...................................................................................................................... 1 3. STRATEGY & AGENCIES INVOLVED ......................................................................... 1 4. WET LAND SYSTEMS ...................................................................................................... 2 4.1 Types of Wetland Systems ............................................................................................... 2 4.2 Wet land system considered for the study ....................................................................... -
Reed Beds for the Treatment of Sewage & Wastewater from Domestic Households
The Use of Reed Beds for the Treatment of Sewage & Wastewater from Domestic Households This document was produced as a community education document for the ratepayers of Lismore City Council. The document is supported by scientific research from Southern Cross University, Lismore, NSW. MAY 2005 TABLE OF CONTENTS 1.0 On-Site Treatment of Domestic Wastewaters....................................................................... 1 1.1 Regulatory Requirements for the Treatment and Disposal of On-Site Wastewater..... 1 1.2 The Treatment Train..................................................................................................... 1 2.0 What is a Reed bed? ........................................................................................................... 2 2.1 How do Reed beds work? ............................................................................................ 2 2.2 Why Install a Reed bed?............................................................................................... 3 3.0 Sizing the Reed Bed ................................................................................................................ 4 3.1 Length to Width Ratio......................................................................................................5 4.0 Construction Considerations .................................................................................................5 4.1 Site Selection................................................................................................................ 5 -
Why Wetlands Are Nature's Superheroes
Key Stage 5 Worksheet Earth LIVE Lessons: Why Wetlands Are Nature’s Superheroes What is it about? Watch the video here: youtu.be/0ZerSvkvpKQ In this video, Dr Christian Dunn, a Senior Lecturer in the School of Natural Sciences at Bangor University, explains why wetland ecosystems are so important for the planet. Open file in your web Dunn discusses the high levels of biodiversity browser to click on the that these ecosystems support and their ability links. to clean water, prevent flooding and help reduce climate change by capturing carbon. What are wetlands? There are many different types of wetlands, including ponds, rivers, lakes, mangrove forests, swamps, bogs and fens. Fens (which get their water from different sources) and bogs (which only receive water from rainfall) are both peatlands, whereas marshes and swamps (forested marshes) are mineral soil-based wetlands. A common feature of all of these habitats is that they form a boundary between truly terrestrial (land) and truly aquatic (or marine) environments. Wetlands are generally divided into two types: coastal, which are saline, and inland, freshwater wetlands. Wetlands provide a significant number of valuable ecosystem services for people, including: • Provision of food (e.g. fish and rice) and building materials (e.g. timber from willow and mangroves) • Flood protection • Carbon sequestration • Water purification • Tourism and leisure opportunities • Fisheries support • Storm protection What are wetlands continued... Ecosystem services are functions of natural habitats that are useful for humans, which also include services such as pollination and the production of oxygen by photosynthetic organisms. Ecosystem services are often assigned an economic value to try to ensure that the loss of natural ecosystems is not disregarded in financial planning, providing an incentive for their protection. -
Milton Keynes Energy Mapping Project - Summary Report
Milton Keynes Energy Mapping Project - Summary Report Final 30 Nov 2012 Centre for Sustainable Energy t. 0117 934 1400 3 St Peter’s Court f. 0117 934 1410 Bedminster Parade [email protected] Bristol BS3 4AQ www.cse.org.uk Registered company no. 2219673 Registered charity no. 298740 Contents Executive Summary .................................................................................................................................................... 4 1 Introduction ....................................................................................................................................................... 8 1.1 Background ................................................................................................................................................ 8 1.2 Terms of reference ..................................................................................................................................... 9 2 Existing low and zero carbon technologies ........................................................................................................10 3 Potential for low and zero carbon technologies ................................................................................................12 3.1 Wind power ..............................................................................................................................................12 3.1.1 Methodology .............................................................................................................................................