Pond Management for Livestock, Fish, and Wildlife
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The Role of a Fish Pond in Optimizing Nutrient Flows in Integrated Agriculture-Aquaculture Farming Systems
The role of a fish pond in optimizing nutrient flows in integrated agriculture-aquaculture farming systems Dang Kieu Nhan Promotor: Prof. Dr. J.A.J. Verreth Hoogleraar Aquacultuur en Visserij Wageningen Universiteit Co-promotor: Dr. M.C.J. Verdegem Universitair Docent, Leerstoelgroep Aquacultuur en Visserij Wageningen Universiteit Promotiecommissie: Prof. Dr. Ir. A.J. van der Zijpp Wageningen Universiteit Dr. M. Ana Milstein Fish and Aquaculture Research Station, Israel Prof. Dr. R. Ruben Radboud Universiteit Nijmegen Prof. Dr. Nguyen Anh Tuan Can Tho University, Vietnam Dit onderzoek is uitgevoerd binnen de onderzoeksschool Wageningen Institute of Animal Sciences (WIAS) The role of a fish pond in optimizing nutrient flows in integrated agriculture-aquaculture farming systems Dang Kieu Nhan Proefschrift ter verkrijging van de graad van doctor op gezag van de rector magnificus van Wageningen Universiteit, Prof. dr. M.J.Kropff, in het openbaar te verdedigen op woensdag 3 oktober 2007 des namiddags te vier uur in de Aula Nhan, D.K., 2007. The role of a fish pond in optimizing nutrient flows in integrated agriculture-aquaculture farming systems. PhD Thesis, Wageningen University, The Netherlands ISBN: 978-90-8504-739-1 Contents Chapter 1 General introduction 1 Chapter 2 Integrated freshwater aquaculture, crop and livestock production in 9 the Mekong Delta, Vietnam: determinants and the role of the pond Chapter 3 Food inputs, water quality and nutrient accumulation in integrated 37 pond systems: a multivariate approach Chapter 4 Water and nutrient budgets of ponds in integrated agriculture- 67 aquaculture systems in the Mekong Delta, Vietnam Chapter 5 Economic and nutrient discharge tradeoffs of excreta-fed 93 aquaculture in the Mekong Delta, Vietnam Chapter 6 General discussion 121 References 133 Summary (English) 145 Summary (Dutch) 149 Summary (Vietnamese) 153 Acknowledgements 157 Training and Supervision Plan 159 Curriculum vitae 160 List of publications 161 Chapter 1 General introduction Chapter 1 1. -
Landscape Character Assessment
OUSE WASHES Landscape Character Assessment Kite aerial photography by Bill Blake Heritage Documentation THE OUSE WASHES CONTENTS 04 Introduction Annexes 05 Context Landscape character areas mapping at 06 Study area 1:25,000 08 Structure of the report Note: this is provided as a separate document 09 ‘Fen islands’ and roddons Evolution of the landscape adjacent to the Ouse Washes 010 Physical influences 020 Human influences 033 Biodiversity 035 Landscape change 040 Guidance for managing landscape change 047 Landscape character The pattern of arable fields, 048 Overview of landscape character types shelterbelts and dykes has a and landscape character areas striking geometry 052 Landscape character areas 053 i Denver 059 ii Nordelph to 10 Mile Bank 067 iii Old Croft River 076 iv. Pymoor 082 v Manea to Langwood Fen 089 vi Fen Isles 098 vii Meadland to Lower Delphs Reeds, wet meadows and wetlands at the Welney 105 viii Ouse Valley Wetlands Wildlife Trust Reserve 116 ix Ouse Washes 03 THE OUSE WASHES INTRODUCTION Introduction Context Sets the scene Objectives Purpose of the study Study area Rationale for the Landscape Partnership area boundary A unique archaeological landscape Structure of the report Kite aerial photography by Bill Blake Heritage Documentation THE OUSE WASHES INTRODUCTION Introduction Contains Ordnance Survey data © Crown copyright and database right 2013 Context Ouse Washes LP boundary Wisbech County boundary This landscape character assessment (LCA) was District boundary A Road commissioned in 2013 by Cambridgeshire ACRE Downham as part of the suite of documents required for B Road Market a Landscape Partnership (LP) Heritage Lottery Railway Nordelph Fund bid entitled ‘Ouse Washes: The Heart of River Denver the Fens.’ However, it is intended to be a stand- Water bodies alone report which describes the distinctive March Hilgay character of this part of the Fen Basin that Lincolnshire Whittlesea contains the Ouse Washes and supports the South Holland District Welney positive management of the area. -
Ecosystem Services Generated by Fish Populations
AR-211 Ecological Economics 29 (1999) 253 –268 ANALYSIS Ecosystem services generated by fish populations Cecilia M. Holmlund *, Monica Hammer Natural Resources Management, Department of Systems Ecology, Stockholm University, S-106 91, Stockholm, Sweden Abstract In this paper, we review the role of fish populations in generating ecosystem services based on documented ecological functions and human demands of fish. The ongoing overexploitation of global fish resources concerns our societies, not only in terms of decreasing fish populations important for consumption and recreational activities. Rather, a number of ecosystem services generated by fish populations are also at risk, with consequences for biodiversity, ecosystem functioning, and ultimately human welfare. Examples are provided from marine and freshwater ecosystems, in various parts of the world, and include all life-stages of fish. Ecosystem services are here defined as fundamental services for maintaining ecosystem functioning and resilience, or demand-derived services based on human values. To secure the generation of ecosystem services from fish populations, management approaches need to address the fact that fish are embedded in ecosystems and that substitutions for declining populations and habitat losses, such as fish stocking and nature reserves, rarely replace losses of all services. © 1999 Elsevier Science B.V. All rights reserved. Keywords: Ecosystem services; Fish populations; Fisheries management; Biodiversity 1. Introduction 15 000 are marine and nearly 10 000 are freshwa ter (Nelson, 1994). Global capture fisheries har Fish constitute one of the major protein sources vested 101 million tonnes of fish including 27 for humans around the world. There are to date million tonnes of bycatch in 1995, and 11 million some 25 000 different known fish species of which tonnes were produced in aquaculture the same year (FAO, 1997). -
Information Sheet on Ramsar Wetlands (RIS)
Information Sheet on Ramsar Wetlands (RIS) Categories approved by Recommendation 4.7 (1990), as amended by Resolution VIII.13 of the 8th Conference of the Contracting Parties (2002) and Resolutions IX.1 Annex B, IX.6, IX.21 and IX. 22 of the 9th Conference of the Contracting Parties (2005). Notes for compilers: 1. The RIS should be completed in accordance with the attached Explanatory Notes and Guidelines for completing the Information Sheet on Ramsar Wetlands. Compilers are strongly advised to read this guidance before filling in the RIS. 2. Further information and guidance in support of Ramsar site designations are provided in the Strategic Framework for the future development of the List of Wetlands of International Importance (Ramsar Wise Use Handbook 7, 2nd edition, as amended by COP9 Resolution IX.1 Annex B). A 3rd edition of the Handbook, incorporating these amendments, is in preparation and will be available in 2006. 3. Once completed, the RIS (and accompanying map(s)) should be submitted to the Ramsar Secretariat. Compilers should provide an electronic (MS Word) copy of the RIS and, where possible, digital copies of all maps. 1. Name and address of the compiler of this form: FOR OFFICE USE ONLY. DD MM YY Joint Nature Conservation Committee Monkstone House City Road Designation date Site Reference Number Peterborough Cambridgeshire PE1 1JY UK Telephone/Fax: +44 (0)1733 – 562 626 / +44 (0)1733 – 555 948 Email: [email protected] 2. Date this sheet was completed/updated: Designated: 28 November 1985 3. Country: UK (England) 4. Name of the Ramsar site: Martin Mere 5. -
World Reference Base for Soil Resources 2014 International Soil Classification System for Naming Soils and Creating Legends for Soil Maps
ISSN 0532-0488 WORLD SOIL RESOURCES REPORTS 106 World reference base for soil resources 2014 International soil classification system for naming soils and creating legends for soil maps Update 2015 Cover photographs (left to right): Ekranic Technosol – Austria (©Erika Michéli) Reductaquic Cryosol – Russia (©Maria Gerasimova) Ferralic Nitisol – Australia (©Ben Harms) Pellic Vertisol – Bulgaria (©Erika Michéli) Albic Podzol – Czech Republic (©Erika Michéli) Hypercalcic Kastanozem – Mexico (©Carlos Cruz Gaistardo) Stagnic Luvisol – South Africa (©Márta Fuchs) Copies of FAO publications can be requested from: SALES AND MARKETING GROUP Information Division Food and Agriculture Organization of the United Nations Viale delle Terme di Caracalla 00100 Rome, Italy E-mail: [email protected] Fax: (+39) 06 57053360 Web site: http://www.fao.org WORLD SOIL World reference base RESOURCES REPORTS for soil resources 2014 106 International soil classification system for naming soils and creating legends for soil maps Update 2015 FOOD AND AGRICULTURE ORGANIZATION OF THE UNITED NATIONS Rome, 2015 The designations employed and the presentation of material in this information product do not imply the expression of any opinion whatsoever on the part of the Food and Agriculture Organization of the United Nations (FAO) concerning the legal or development status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries. The mention of specific companies or products of manufacturers, whether or not these have been patented, does not imply that these have been endorsed or recommended by FAO in preference to others of a similar nature that are not mentioned. The views expressed in this information product are those of the author(s) and do not necessarily reflect the views or policies of FAO. -
Holme Fen Nature Reserve the Lost Lake and Other
Today, Holme Fen is the largest lowland Once the Mere had been 3 The gamekeeper’s plantation drained, over half the silver birch woodland in England, but it has After the drainage, Holme Fen was not farmed had a very different history. wildlife recorded in the area became extinct here. because it was still too wet and boggy. As it One example was the dried out, Holme Fen turned from reeds to 1 Whittlesea Mere and the Holme Posts Swallowtail butterfly raised bog and then to birch woodland. Swallowtail butterfly. by Matt Berry The ground beneath your feet was once level with 2 Disappearing houses Earlier this century, this area was used for the top of the Holme Posts. At that time, game. In the gamekeeper’s plantation (also One of the most dramatic changes here has been Whittlesea Mere was a short distance away to the know as ‘Ballard’s Covert’) you will see a mix of the drop in ground levels following the drainage, as east. At three miles across, it was a spectacular different trees including oak, birch, and alder. the peat dried out and eroded. Tony Redhead, sight - the largest lake in lowland England. whose family grew up here, remembers some of The variety of trees makes it a good place to You might have come to the effects: hear and see woodland birds, such as Blackcaps, take part in one of the "There was one house, in the 1950s, that had to Woodpeckers and Redpolls. Holme Fen was famous ice skating races be pulled down because you could walk bought for the nation in 1952. -
Water Quality Guidelines for the Management of Pond Fish Culture
International Journal of Environment Sciences Vol. 5 No.INTERNATIONAL 2 (July-December, 2019) JOURNAL OF ENVIRONMENTAL SCIENCES Volume 3, No 6, 2013 Received:© Copyright 14th May by 2019the authors Revised: - Licensee 30th June IPA 2019- Under Accepted: Creative 15th Commons July 2019 license 3.0 Research article ISSN 0976 – 4402 Water quality guidelines for the management of pond fish culture Anita Bhatnagar, Pooja Devi Department of Zoology, Kurukshetra University, Kurukshetra, India-136119 [email protected] doi: 10.6088/ijes.2013030600019 ABSTRACT The Optimum fish production is totally dependent on the physical, chemical and biological qualities of water to most of the extent. Hence, successful pond management requires an understanding of water quality. Water quality is determined by variables like temperature, transparency, turbidity, water colour, carbon dioxide, pH, alkalinity, hardness, unionised ammonia, nitrite, nitrate, primary productivity, BOD, plankton population etc. In the present chapter water quality management principles in fish culture have been reviewed to make aware the fish culturist and environmentalist about the important water quality factors that influence health of a pond and are required in optimum values to increase the fish yields to meet the growing demands of present day scenario of the world, when the food resources are in a state of depletion and the population pressure is increasing on these resources. Keywords: Assessment and Monitoring, Culture, Fish productivity, Parameters, Water quality 1. Introduction Fish is an inexpensive source of protein and an important cash crop in many regions of world and water is the physical support in which they carry out their life functions such as feeding, swimming, breeding, digestion and excretion (Bronmark and Hansson, 2005). -
Fish Culture in Brackish Water
Fish Culture in Brackish Water. Item Type Journal Contribution Authors Nzioka, R.M. Download date 01/10/2021 17:26:10 Link to Item http://hdl.handle.net/1834/7089 POST KENYA v.5 no. 2 May-August 1980 FISH CULTURE IN BRACKISH WATER R. M. Nzioka, Ketrya Marine and Fisheries Research Institute Introduction loose initial structure of the mud changes as moisture Brackish water is a mixture of fresh and salty water is diminished by evaporation and transpiration. The which usually occurs in estuaries, and has a salinity process of drying out results in the shrinking of the soil usually of between 15 and 30 per thousand, depending wItil it attains the proper physical character of pond on rainfall and freshwater run-off. barrier. Even though ponds very close to the shore are Some fish species like mullets are able to survive filled with undiluted seawater the great amount of rain in this environment. Most of the Mugi/idae shoal swim water trapped in the ponds during the monsoons, makes in or near the surface of the water and may be seen it not possible for salinity values equal or higher than jumping repeatedly in estuaries usually in the evenings. those of seawater to occur in the ponds at any time M. cepha/us and Liza aurata are potential species for other than during prolonged periods of drought. culture. These species occur in vast numbers and have very firm flesh of excellent flavour. They spawn in the Aquaculture tropics mostly from September to October. During this period they migrate away from estuaries. -
Understanding Your Fish Pond Water Analsysis Report
Cooperative Aquaculture/Fisheries Extension Program University of Arkansas at Pine Bluff Understanding Your Fish Pond Water Analysis Report Nathan M. Stone Figure 1 Extension Fisheries Water Analysis Report: Fish Specialist (Example) Hugh K. Thomforde pH - - - - - - - - - - - - - - - - - - - - - - - - - - -7.24 Extension Aquaculture Some sportfish and aquaculture Electrical Conductivity - - -205 mSiemens/cm Specialist pond owners choose to submit water Alkalinity, Total - - - - - 100.00 mg/l as CaCO3 samples to the University of Hardness, Total - - - - -103.80 mg/l as CaCO3 Arkansas Cooperative Extension CO (Carbonate) - - - - - 0.09 mg/l as CaCO Service for analysis. The water 3 3 samples are mailed to the Water HCO3 (Bicarbonate) - - 99.90 mg/l as CaCO3 Quality Laboratory, Arkansas Water Fe (Iron) - - - - - - - - - - - - - - - - - - -0.05 mg/l Resources Center, University of Mn (Manganese) - - - - - - - - - - - - -0.01 mg/l Arkansas at Fayetteville. The labora F (Fluoride) - - - - - - - - - - - - - - - - -0.15 mg/l tory tests the water and sends the Cl (Chloride) - - - - - - - - - - - - - - - - -3.13 mg/l results back. Below are some guide lines for interpreting those results. SO4 (Sulfate) - - - - - - - - - - - - - - - - 3.21 mg/l These guidelines describe how to NO3 (Nitrate) - - - - - - - - - - - - - - - - 0.04 mg/l interpret results for both surface NO3-N (Nitrate-Nitrogen) - - - - - - - 0.01 mg/l waters and ground waters. Surface NH -N (Ammonia-Nitrogen) - - - - - 0.11 mg/l waters are those exposed to the air 3 and sunlight, such as streams, ponds, NO2-N (Nitrite-Nitrogen) - - - - - - - - 0.00 mg/l reservoirs and lakes. Ground waters PO4 (Phosphate) - - - - - - - - - - - - - 0.06 mg/l are waters from wells or springs tapping underground aquifers and are often devoid of dissolved oxygen. These waters may also contain high levelsInterpreting of dissolved Results gasses or iron. -
Pokagon State Park Guide
KETTLES AND KAMES The distinctive landscape of Indiana’s Pokagon State Park is a legacy of the most recent Ice Age. Although the Pleistocene Epoch began about 2.6 million years ago, today one can see only the effects of the most recent continental glacier from the Wisconsin age. The irregularly shaped hills, bogs, and lakes are underlain by an assortment of materials that melted from a rugged disintegrating ice sheet a mere 14,000 years ago. Kettle lakes Lake Lonidaw is one of the kettle lakes that formed as the Wisconsin-age glacier retreated. Large blocks of ice broke free from the glacier and were buried under insulating debris. The ice slowly melted, leaving behind a water-filled depression. Morainal landscape The steeply rolling hills, bogs, and interconnected lakes of the park bear witness to the massive ice sheets that advanced over and then melted from this part of the Midwest. & Water Survey. Glacial erratics This former Canadian resident arrived in one of the glacial advances into central Indiana. Many of these trans- ported rocks and boulders, known as “glacial erratics,” are in evidence throughout the park. Lake James THE GEOLOGIC STORY The Northern Moraine and Lake Region, in which Pokagon State Park is located, is noted of Pokagon State Park for its beautiful scenery and lakes — a land- scape created by glaciers. The third largest natural lake in Indiana, Lake James covers 1,140 acres and is 88 feet deep. It is one of the many kettle lakes in the region and was formed by the slow melting of a buried ice block. -
Maine's Coastal Wetlands
Program Support from: Maine Department of Environmental Protection NOAA Coastal Services Center Maine Coastal Program, Maine State Planning Office Maine Department of Marine Resources MAINE'S COASTAL WETLANDS: I. TYPES, DISTRIBUTION, RANKINGS, FUNCTIONS AND VALUES by Alison E. Ward NOAA Coastal Management Fellow Bureau of Land & Water Quality Division of Environmental Assessment Augusta, ME September 1999 DEPLW1999 - 13 TABLE OF CONTENTS Page # ACKNOWLEDGEMENTS .........................................................................................................................ii SUMMARY..................................................................................................................................................iii INTRODUCTION ........................................................................................................................................ 1 COASTAL DEVELOPMENT..................................................................................................................... 7 NRPA PERMITTED ACTIVITY IN COASTAL WETLANDS ............................................................................... 8 NRPA PERMITTED ACTIVITY IN COASTAL WETLANDS BY REGIONAL OFFICE .......................................... 11 COASTAL WETLAND IMPACT..................................................................................................................... 14 TYPES & DISTRIBUTION OF INTERTIDAL HABITATS................................................................. 17 TYPES AND ACREAGE OF INTERTIDAL -
Information About the Habitat Use of Salines and Fish Ponds by Wintering
Informationabout the habitatuse of salinesand fish pondsby winteringwaders in CadizBay, southwest Spain A. Perez-Hurtado & F. Hortas Perez-Hurtado,A. & Hortas,F. 1991. Informationabout the habitat use of salinesand fish ponds bywintering waders in CadizBay, southwest Spain. WaderStudy Group Bull. 66: 48-53. CadizBay, recently declared as a NaturalPark, is an importantarea for wintering waders in Spain. In the lastfew years mudflats and salines in Cadiz Bay have been claimed for human activities with adverseimpacts on their shorebird populations. Thus, the importance to shorebirdsof thesalines andfish ponds adjacent to theBay could be increasingif they are usedas alternativefeeding areas. In generalthe birds used the salines and fish ponds both for feeding and roosting: some 66% of wadersin salinesat lowtide were feeding. However,not all the birdsused the differenthabitats in thesame way or at thesame state of tide. Someimplications of the usemade by waders of these areasto theirenergetic requirements, morphological adaptations and prey availability are discussed. A. Perez-Hurtado& F. Hodas,Laboratorio de BiologiaMarina, Apto. de Fisiologiay Biologia Animal,Facultad de Biologia,Universidad de Sevilla,Aptdo 1095, E-41080, Spain. INTRODUCTION Thewetlands of CadizBay (between 36ø23'N, 6ø08'W and 36ø37'N,6ø15'W, southwest Spain) extend over 18,000 ha, sall•es la tapa andinclude many different and productivehabitats; intertidal mudflats,salines, fish ponds, lagoons and semi-natural salt marshes(Figure 1). Thesesupport a largenumber of winter-