Genes to Ecosystems: Exploring the Frontiers of Ecology with One of the Smallest Biological Units
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Efficacy of Using Electrofishing to Reduce Recruitment of Invasive Common Carp in Malheur Lake, a Large Endorheic Marsh
U.S. Fish and Wildlife Service Efficacy of using electrofishing to reduce recruitment of invasive Common Carp in Malheur Lake, a large endorheic marsh Final Report May 2017 By William Simpson, Doug Peterson , and Kurt Steinke Abernathy Fish Technology Center Longview, Washington Linda Beck1 Malheur Naonal Wildlife Refuge Princeton, Oregon 1 Current address: U.S. Fish and Wildlife Service, Fisheries and Aquac Conservaon, Portland, Oregon Adult Common Carp from Malheur Lake Developing embryos of Common Carp Abstract Concern about electrofishing inadvertently harming the embryos of species of conservation concern has motivated much of the research that describes what electrical conditions can kill fish embryos. As a result, targeted electrofishing might be underutilized as a potential control method to reduce the recruitment of nuisance or invasive fishes like Common Carp (Cyprinus carpio). Common Carp are one of the most widely distributed invasive fish in North America, and biologist are turning to integrated pest management techniques and targeting multiple life stages because control efforts based solely on removal of adults have often been unsuccessful. We examined changes in the survival of invasive Common Carp embryos while manipulating the transfer of electric power to the embryos by shocking them in water from carp-occupied areas using a variety of voltage gradient and waveform treatments produced by commercial electrofishing units and generators. Survival of electroshocked Common Carp embryos was < 50% at power densities (12,700 -
Diel Horizontal Migration of Zooplankton: Costs and Benefits Of
Freshwater Biology (2002) 47, 343–365 FRESHWATER BIOLOGY SPECIAL REVIEW Diel horizontal migration of zooplankton: costs and benefits of inhabiting the littoral R. L. BURKS,* D. M. LODGE,* E. JEPPESEN† and T. L. LAURIDSEN† *Department of Biological Sciences, University of Notre Dame, Notre Dame, IN, U.S.A. †Department of Lake and Estuarine Ecology, National Environmental Research Institute, Vejlsøvej, Silkeborg, Denmark SUMMARY 1. In some shallow lakes, Daphnia and other important pelagic consumers of phyto- plankton undergo diel horizontal migration (DHM) into macrophytes or other structures in the littoral zone. Some authors have suggested that DHM reduces predation by fishes on Daphnia and other cladocerans, resulting in a lower phytoplankton biomass in shallow lakes than would occur without DHM. The costs and benefits of DHM, and its potential implications in biomanipulation, are relatively unknown, however. 2. In this review, we compare studies on diel vertical migration (DVM) to assess factors potentially influencing DHM (e.g. predators, food, light, temperature, dissolved oxygen, pH). We first provide examples of DHM and examine avoidance by Daphnia of both planktivorous (PL) fishes and predacious invertebrates. 3. We argue that DHM should be favoured when the abundance of macrophytes is high (which reduces planktivory) and the abundance of piscivores in the littoral is sufficient to reduce planktivores. Food in the littoral zone may favour DHM by daphnids, but the quality of these resources relative to pelagic phytoplankton is largely unknown. 4. We suggest that abiotic conditions, such as light, temperature, dissolved oxygen and pH, are less likely to influence DHM than DVM because weaker gradients of these conditions occur horizontally in shallow lakes relative to vertical gradients in deep lakes. -
Lake Restoration and Biomanipulation in Temperate Lakes: Relevance for Subtropical and Tropical Lakes By
In: (Ed. V. Reddy), Tropical eutrophic lakes: their restoration and management (in press). Lake restoration and biomanipulation in temperate lakes: relevance for subtropical and tropical lakes by Erik Jeppesen1.2*, Martin Søndergaard1, Nestor Mazzeo3, Mariana Meerhoff3, Christina C. Branco4, Vera Huszar5 and Flavio Scasso3 1)National Environmental Research Institute, Dept. of Freshwater Ecology, Vejlsøvej 25, DK-8600 Silkeborg, Denmark 2) Dept. of Botanical Ecology, University of Aarhus, Nordlandsvej 68, DK-8230 Risskov, Denmark 3) Sección Limnología, Departamento de Ecología, Facultad de Ciencias, Iguá 4225, Montevideo, Uruguay 4) Universidade do Rio de Janeiro, Depto. Ciências Naturais, Av. Pasteur 458, 22290-240 Rio de Janeiro, Brazil 5) Universidade Federal do Rio de Janeiro, Museu Nacional, Departamento de Botânica, Laboratório de Ficologia. Quinta da Boa Vista, São Cristóvão, Rio de Janeiro, Brasil, 20940-040. *Corresponding author: [email protected] Keywords: lakes, restoration, biomanipulation, temperate, subtropical, tropical Abstract This introductory chapter to the book “Tropical eutrophic lakes: their restoration and management” gives a summary survey of the responses of temperate lakes to increased nutrient loading (the eutrophication process) and during remediation. Chemically and biologically conditioned resistance may cause a delayed response to the nutrient loading reduction and different methods of overcoming this resistance are briefly described. Biological restoration methods (termed “biomanipulation”) are promising new tools. However, a significant difference in biological interactions in temperate versus subtropical-tropical lakes renders it difficult directly to apply the biological restoration methods. These include often higher dominance and abundance of small fish, higher aggregation of fish in vegetation, higher number of fish cohorts per year, higher degree of omnivorous feeding by fish and less piscivory in subtropical and tropical lakes than in temperate lakes. -
From Darkness to Light the Restoration of Barton Broad
From darkness to light the restoration of Barton Broad Contents Map 2 Introduction 3 The restoration of Barton Broad 4 Project objectives 5 Methodology and results 6 Suction dredging Lower phosphorus levels in the sediment Lower phosphorus levels in the water Change in the algae Securing water space for recreation Biomanipulation 12 Creating clear water Reducing wave energy Re-growth of aquatic plants Reed margin restoration 16 Additional restoration work 17 Visiting Barton Broad 18 What happens next? 19 Glossary 19 More reading 20 2 River Ant Barton Turf North The Heater 0 1/2 mile 0 0.5 km Barton Fish barriers Broad Boardwalk Gay's staithe and Ra solar boat trip Pleasure Island Herons' Carr very wet woodland Neatishead viewing platform Turkey toilets and car park Broad River Ant for solar boat trip and for the Herons' Carr car park for boardwalk with disabled people viewing platform Irstead 3 Introduction Clear Water 2000 was the Broads Authority’s millennium project to restore the clear water and landscape of Barton Broad, encourage back the wildlife, and improve and expand access to this beautiful broad. Barton Broad is owned by the Norfolk Wildlife Trust and is the second largest of the broads. It is a national treasure, as a National Nature Reserve and international site for wildlife conservation, and as an important site for boating and sailing for many local people and visitors. Research and monitoring has formed an essential part of the Barton Broad restoration project, and this document sets out its results. Investigation of nutrient budgets, sediment nutrient release and creation of clear water areas were part of the research programme, which informed the project’s inception, development and success. -
Greater Annual Macrophyte Abundance in Warmer Locations in Consequence of Nutrients in Lakes V205a Page 2 the Longer Plant Growing-Season
Nutrients in Lakes V205a Page 1 Reference Type: Journal Article Record Number: 482 Author: Moss, B.; Stephen, D.; Balayla, D. M.; Becares, E.; Collings, S. E.; Fernandez-Alaez, C.; Fernandez-Alaez, M.; Ferriol, C.; Garcia, P.; Goma, J.; Gyllstroem, M.; Hansson, L. A.; Hietala, J.; Kairesalo, T.; Miracle, M. R.; Romo, S.; Rueda, J.; Russell, V.; Stahl-Delbanco, A.; Svensson, M.; Vakkilainen, K.; Valentin, M.; Van De Bund, W. J.; Van Donk, E.; Vicente, E.; Villena, M. J. Year: 2004 Title: Continental-scale patterns of nutrient and fish effects on shallow lakes: Synthesis of a pan-european mesocosm experiment Journal: Freshwater Biology Volume: 49 Issue: 12 Pages: 1633-1649 Accession Number: AN 2005:18924 Abstract: 1. Results are analyzed from 11 expts. in which effects of fish addn. and nutrient loading on shallow lakes were studied in mesocosms. The expts., five in 1998, six in 1999, were carried out in six lakes, distributed from Finland to southern Spain, according to a std. protocol. 2. Effects of the treatments on 29 std. chem., phytoplankton and zooplankton variables are examd. to assess the relative importance of bottom-up (nutrient enrichment) and top-down (fish predation) effects. For each year, the expts. in different locations are treated as replicates in a meta-anal. Results of individual expts. are then compared in terms of the patterns of significant influences of nutrient addn. and fish predation with these overall results (the baseline), and between years in the same location. 3. The overall meta-anal. gave consistent results across the 2 years, with nutrient loading influencing all of the chem. -
Searching Explanations of Nature in the Mirror World of Math
Table of Contents Searching Explanations of Nature in the Mirror World of Math........................................................................0 ABSTRACT...................................................................................................................................................0 INTRODUCTION.........................................................................................................................................0 FLIPPING LAKES........................................................................................................................................1 THE TROPHIC CASCADE..........................................................................................................................6 CHAOS IN PLANKTON DYNAMICS......................................................................................................12 SO, WHAT DO MODELS REALLY TELL US?.......................................................................................13 THEORY AS A BRIDGE BETWEEN DISCIPLINES..............................................................................15 RESPONSES TO THIS ARTICLE.............................................................................................................16 Acknowledgments:.......................................................................................................................................16 LITERATURE CITED................................................................................................................................17 -
Biomanipulation of Plants and Fish to Restore Lake Parkinson: a Case Study and Its Implications
Pages 53-65 in Collier, K.J. (Ed), 1994. Restoration of Aquatic Habitats. Selected papers from the second day of the New Zealand Limnological Society 1993 Annual Conference. Department of Conservation. BIOMANIPULATION OF PLANTS AND FISH TO RESTORE LAKE PARKINSON: A CASE STUDY AND ITS IMPLICATIONS D. K. Rowe and P. D. Champion NIWA, P.O. Box 11-115, Hamilton ABSTRACT The biomanipulation of aquatic plants and fish was successfully used to restore recreational uses of Lake Parkinson, a small (1.9 ha) dune lake, southwest of Auckland, after it had been degraded by introductions of exotic plant and fish species. The oxygen weed Egeria densa was eradicated by stocking a herbivorous fish, the grass carp, Ctenopharyngodon idella. Complete removal of all plants in this lake enabled the subsequent restructuring of its fish fauna. All fish species including the stocked grass carp, rudd (Scardinius erythrophthalmus), tench (Tinca tinca), the native smelt (Retropinna retropinna) and the common bully (Gobiomorphus cotidianus) were removed following application of the piscicide, rotenone. After removal of the grass carp, communities of native macrophytes regenerated from senescent seeds in the lake-bed sediment. The common bully was re-established in the lake by stocking to provide a forage fish for trout. Lake Parkinson now supports a valuable put-and-take trout fishery and is free from problems caused by exotic macrophytes. The combination of biomanipulation techniques used in Lake Parkinson has the potential to restore recreational values of other small lakes, to help protect rare native macrophyte and fish species threatened by invasions of exotic species, to restructure fish populations, and to minimise the spread of unwanted exotic plant and fish species. -
Biomanipulation of Lake Ecosystems: Successful Applications and Expanding Complexity in the Underlying Science
Freshwater Biology (2002) 47, 2453–2465 Biomanipulation of lake ecosystems: successful applications and expanding complexity in the underlying science THOMAS MEHNER,* JU¨ RGEN BENNDORF,† PETER KASPRZAK* and RAINER KOSCHEL* *Leibniz-Institute of Freshwater Ecology and Inland Fisheries, Berlin, Germany †Dresden University of Technology, Institute of Hydrobiology, Dresden, Germany SUMMARY 1. To illustrate advances made in biomanipulation research during the last decade, seven main topics that emerged after the first biomanipulation conference in 1989 are discussed in relation to the papers included in this special issue and the general literature. 2. The substantially higher success rates of biomanipulations in shallow as opposed to stratified lakes can be attributed to several positive feedback mechanisms relating mainly to the recovery of submerged macrophytes. 3. The role of both nutrient loading and in-lake concentrations in predicting the success of biomanipulations is emphasised and supported by empirically defined threshold values. Nutrient recycling by aquatic organisms (such as fish) can contribute to the bottom-up effects on lake food webs, although the degree can vary greatly among lakes. 4. Ontogenetic niche shifts and size-structured interactions particularly of fish populations add to the complexity of lake food webs and make scientifically sound predictions of biomanipulation success more difficult than was previously envisaged. 5. Consideration of appropriate temporal and spatial scales in biomanipulation research is crucial to understanding food web effects induced by changes in fish communities. This topic needs to be further developed. 6. An appropriate balance between piscivorous, planktivorous and benthivorous fishes is required for long-lasting success of biomanipulations. Recommended proportions and absolute densities of piscivorous fish are currently based on data from only a few biomanipulation experiments and need to be corroborated by additional and quantitative assessments of energy flow through lake food webs. -
Hoveton Great Broad Restoration Project: Seasonal Comparative Fish Areas
a) Ecological condition of Hoveton Great Broad and Hudson's Bay The notified features for Hoveton Great Broad and Hudson’s Bay are: • H3140 Hard oligo-mesotrophic waters with benthic veg of Chara spp Aerial view of algal blooms on Hoveton • Great Broad and Hudson’s Bay. H3150 Natural eutrophic lakes with Magnopotamion or Hydrocharition b) • S1355 Otter, Lutra lutra © Mike Page. They are currently classified as ‘unfavourable – no change’ and ‘poor ecological status’ under the Habitats Directive and the Water Framework Directive respectively due to high turbidity, low macrophyte diversity and abundance, and the associated impact on aquatic fauna. Theses conditions can be directly attributed to historic eutrophication, in particular phosphate from sewage treatment The Hoveton Wetlands Restoration Project aims to deliver the works (Moss 1983). In the Broads, as with many other shallow lakes in north west Europe, this has resulted in: Figure 1: Macrophyte abundance (a) and diversity (b) of key lakes in the Broads 2014-2018, Hoveton Great Broad highlighted. Broads Authority water plant monitoring (Tomlinson et al. 2019). restoration of Hoveton Great Broad and Hudson’s Bay. These Aerial view of Hoveton Great Broad and Hudson’s Bay • high levels of phytoplankton production (often including blooms of blue green algae) lakes are situated in Norfolk, UK within The Broads National Park. • a reduction and eventually almost complete loss of aquatic plant cover and diversity They form part of the Bure Broads and Marshes, the Broadland SPA and the Broads SAC, and Broadland Ramsar Site. • high rates of sedimentation • dominance by small open water zooplankton species and loss of plant-associated invertebrates The project is using a combination of sediment removal and biomanipulation of the fish community to restore clear water • simplification of the structure of the fish community and dominance by a small number of age classes of and macrophytes to these lakes, restoring their natural ecological function. -
Factors Affecting Water Plant Recovery - A
Factors affecting water plant recovery - A. Overview and sediment influences author: J. Schutten' co-authors: A.J. Davy-,F.J.Madqwick-, H. COOpS3, W. Admiraal', E.H.R.R.Lammens3, G.L. Phillips> Project No LIFE92-3/UKl031 RIZA project EHS*WATERPLANT ISBN 0948119403 'University of Amsterdam, ARISE, Department of Aquatic Ecotoxicolgy, Kruislaan 320, 1098 SM, Amsterdam, The Netherlands 2University of East Anglia, School of Biological Sciences, NR4 7TJ, Norwich, UK 3RIZA (Institute for Inland Water Management and Waste Water Treatment), P.D. Box 17, 8200 AA, Lelystad, The Netherlands 4The Broads Authority, Thomas Harvey House, 18 Colegate, NR3 1BQ, Norwich, UK 5Environment Agency (former National Rivers Authority), Cobham Road, IP3 9JE, Ipswich, UK This report should be cited as: Schutten, J. Davy, A. J., Madgwick, F.J., Coops, H., Admiraal, W., Lammens, E.H.R.R., and Phillips, G.L. (1997) Factors affecting water plant recovery - overview and sediment influences. In Madgwick, F.J. & Phillips, G. L. (eds) 'Restoration of the Norfolk Broads - Final Report', (BARS14) Broads Authority and (P-89) Environment Agency, Norwich UK. Commissioning Organisations: Broads Authority, Thomas Harvey House, 18 Colegate, Norwich, Norfolk, NR3 1BQ, UK Tel: +44 (0) 1603610734 Fax: +44 (0) 1603765710 Environment Agency, Kingfisher House, Goldhay Way, Orton Goldhay, Peterborough, PE2 5ZR, UK Tel: +44 (0) 1733371811 Fax: +44 (0) 1733231840 ©European Commission, Broads Authority, RIZA and Environment Agency 1997. All rights reserved. No part of this publication may be reproduced, stored in a retrieval system, or transmitted in any form or by any means, electronic, mechanical, photocopying, recording or otherwise without the prior permission of European Commission, The Broads Authority, RIZA and the Environment Agency. -
Review of the Potential for Biomanipulation of Phytoplankton Abundance by Freshwater Mussels (Kakahi) in the Te Arawa Lakes
Review of the potential for biomanipulation of phytoplankton abundance by freshwater mussels (kakahi) in the Te Arawa lakes NIWA Client Report: HAM2006-125 January 2007 NIWA Project: BOP07211 Review of the potential for biomanipulation of phytoplankton abundance by freshwater mussels (kakahi) in the Te Arawa lakes Ngaire Phillips Prepared for Environment Bay of Plenty NIWA Client Report: HAM2006-125 January 2007 NIWA Project: BOP07211 National Institute of Water & Atmospheric Research Ltd Gate 10, Silverdale Road, Hamilton P O Box 11115, Hamilton, New Zealand Phone +64-7-856 7026, Fax +64-7-856 0151 www.niwa.co.nz All rights reserved. This publication may not be reproduced or copied in any form without the permission of the client. Such permission is to be given only in accordance with the terms of the client's contract with NIWA. This copyright extends to all forms of copying and any storage of material in any kind of information retrieval system. Contents Executive Summary iv 1. Introduction 1 2. Background information 2 2.1 General biology 2 2.2 Life cycle 3 2.3 Parasites/predators 5 2.4 Shell morphology 5 2.5 Biomonitoring 6 3. Biomanipulation 8 3.1 Can freshwater mussels be increased to levels in the Te Arawa lakes where they would significantly reduce algal biomass. 8 3.2 Would this be effective for blue-green algal biomass? 12 3.3 Would this affect other species? 13 3.4 Would this affect nutrient levels in the lakes? 14 3.5 Are there other freshwater mussels (native or exotic) or other species that could be effective? 14 4. -
Biomanipulation of Lake Ecosystems: an Introduction
Freshwater Biology (2002) 47, 2277–2281 Biomanipulation of lake ecosystems: an introduction P. KASPRZAK,* J. BENNDORF,† T. MEHNER‡ and R. KOSCHEL* *Department of Limnology of Stratified Lakes, Leibniz-Institute of Freshwater Ecology and Inland Fisheries, Neuglobsow, Germany †Institute of Hydrobiology, Dresden University of Technology, Dresden, Germany ‡Department of Biology and Ecology of Fish, Leibniz-Institute of Freshwater Ecology and Inland Fisheries, Berlin, Germany SUMMARY 1. This paper is an introduction to a special issue of Freshwater Biology containing selected papers from an international symposium on Food Web Effects of Fish in Lake Ecosystems: Research Progress, Water Quality and Fisheries Management held from 31 May to 3 June 2000 in Rheinsberg, Germany. The primary goal of the workshop was to enlarge the current view of fish-induced effects on lake ecosystems. An additional goal was to promote biomanipulation as a multiple-use tool for managing freshwater ecosystems. 2. The three main topics addressed at the workshop were: (i) mechanisms involved in biomanipulation, (ii) whole-lake case studies and (iii) management aspects in water quality and fisheries. 3. Mortality of Daphnia, nutrient recycling, habitat selection and fish predation are reported as important mechanisms governing food-web effects as a result of biomanip- ulation. 4. Whole-lake case studies indicate that repeated fish removal can help improve water quality of shallow lakes, but successful biomanipulation of deep, thermally stratifying lakes remains difficult. 5. In many cases, biomanipulation of lakes has proved to provide benefits in addition to improving water quality. As all lake users are potentially affected when biomanipulation is used as a lake management tool, their concerns need to be clearly recognised if biomanipulation is to be successful in practice.