1
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Harris TD, Reinl KL, Azarderakhsh M, Berger SA, Berman MC, Bizic M, Bhattacharya R, Burnet SH, Cianci-Gaskill JA, Domis LNDS, Elfferich I, Ger KA, Grossart HPF, Ibelings BW, Ionescu D, Kouhanestani ZM, Mauch J, McElarney YR, Nava V, North RL, Ogashawara I, Paule-Mercado MCA, Soria-Píriz S, Sun X, Trout-Haney JV, Weyhenmeyer GA, Yokota K, Zhan Q. What makes a cyanobacterial bloom disappear? A review of the abiotic and biotic cyanobacterial bloom loss factors. Harmful Algae 2024; 133:102599. [PMID: 38485445 DOI: 10.1016/j.hal.2024.102599] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 11/10/2023] [Revised: 01/31/2024] [Accepted: 02/05/2024] [Indexed: 03/19/2024]
Abstract
Cyanobacterial blooms present substantial challenges to managers and threaten ecological and public health. Although the majority of cyanobacterial bloom research and management focuses on factors that control bloom initiation, duration, toxicity, and geographical extent, relatively little research focuses on the role of loss processes in blooms and how these processes are regulated. Here, we define a loss process in terms of population dynamics as any process that removes cells from a population, thereby decelerating or reducing the development and extent of blooms. We review abiotic (e.g., hydraulic flushing and oxidative stress/UV light) and biotic factors (e.g., allelopathic compounds, infections, grazing, and resting cells/programmed cell death) known to govern bloom loss. We found that the dominant loss processes depend on several system specific factors including cyanobacterial genera-specific traits, in situ physicochemical conditions, and the microbial, phytoplankton, and consumer community composition. We also address loss processes in the context of bloom management and discuss perspectives and challenges in predicting how a changing climate may directly and indirectly affect loss processes on blooms. A deeper understanding of bloom loss processes and their underlying mechanisms may help to mitigate the negative consequences of cyanobacterial blooms and improve current management strategies.
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Affiliation(s)
- Ted D Harris
- Kansas Biological Survey and Center for Ecological Research, University of Kansas, 2101 Constant Ave., Lawrence, KS, 66047
| | - Kaitlin L Reinl
- Lake Superior National Estuarine Research Reserve, University of Wisconsin - Madison Division of Extension, 14 Marina Dr, Superior, WI 54880
| | - Marzi Azarderakhsh
- Department of Construction and Civil Engineering, New York City College of Technology, 300 Jay Street, New York, NY 11201
| | - Stella A Berger
- Department of Plankton and Microbial Ecology, Leibniz Institute of Freshwater Ecology and Inland Fisheries, Zur alten Fischerhütte 2, 16775 Stechlin, Germany
| | - Manuel Castro Berman
- Center for Biotechnology and Interdisciplinary Studies, Rensselaer Polytechnic Institute, Troy, NY 12180 and Darrin Freshwater Institute, Rensselaer Polytechnic Institute, Bolton Landing, NY, 12814
| | - Mina Bizic
- Department of Plankton and Microbial Ecology, Leibniz Institute of Freshwater Ecology and Inland Fisheries, Zur alten Fischerhütte 2, 16775 Stechlin, Germany
| | - Ruchi Bhattacharya
- Department of Biological, Geological & Environmental Sciences, Cleveland State University, Cleveland, OH 44115
| | - Sarah H Burnet
- University of Idaho, Fish and Wildlife Sciences, Moscow, ID, USA, 83844
| | - Jacob A Cianci-Gaskill
- Old Woman Creek National Estuarine Research Reserve, Ohio Department of Natural Resources, 2514 Cleveland Rd East, Huron, OH 44839
| | - Lisette N de Senerpont Domis
- Department of Aquatic Ecology, Netherlands Institute of Ecology (NIOO-KNAW), P.O. Box 50, 6708 PB Wageningen, The Netherlands; Department of Water Resources and Pervasive Systems Group, faculty of EEMCS and ITC, University of Twente, The Netherlands
| | - Inge Elfferich
- Cardiff University, Earth and Environmental Sciences, Main Building, Park Place CF10 3AT, Cardiff, UK
| | - K Ali Ger
- Department of Ecology, Center for Biosciences, Universidade Federal do Rio Grande do Norte, R. das Biociencias, Lagoa Nova, Natal, RN, 59078-970, Brazil
| | - Hans-Peter F Grossart
- Department of Plankton and Microbial Ecology, Leibniz Institute of Freshwater Ecology and Inland Fisheries, Zur alten Fischerhütte 2, 16775 Stechlin, Germany; Potsdam University, Institute of Biochemistry and Biology, Maulbeeralle 2, 14469 Potsdam, Germany
| | - Bas W Ibelings
- Department F.-A. Forel for Environmental and Aquatic Sciences, University of Geneva, 66 Blvd Carl Vogt, 1205, Geneva, Switzerland
| | - Danny Ionescu
- Department of Plankton and Microbial Ecology, Leibniz Institute of Freshwater Ecology and Inland Fisheries, Zur alten Fischerhütte 2, 16775 Stechlin, Germany
| | - Zohreh Mazaheri Kouhanestani
- School of Natural Resources, University of Missouri-Columbia, Anheuser-Busch Natural Resources Building, Columbia, MO, 65211-7220
| | - Jonas Mauch
- Department of Community and Ecosystem Ecology, Leibniz Institute of Freshwater Ecology and Inland Fisheries, Müggelseedamm 301, 12587 Berlin, Germany
| | - Yvonne R McElarney
- Fisheries and Aquatic Ecosystems, Agri-Food and Biosciences Institute, Belfast, Northern Ireland
| | - Veronica Nava
- Department of Earth and Environmental Sciences, University of Milano-Bicocca, Piazza della Scienza 1, 20126 Milano, MI, Italy.
| | - Rebecca L North
- School of Natural Resources, University of Missouri-Columbia, Anheuser-Busch Natural Resources Building, Columbia, MO, 65211-7220
| | - Igor Ogashawara
- Department of Plankton and Microbial Ecology, Leibniz Institute of Freshwater Ecology and Inland Fisheries, Zur alten Fischerhütte 2, 16775 Stechlin, Germany
| | - Ma Cristina A Paule-Mercado
- Institute of Hydrobiology, Biology Centre of the Czech Academy of Sciences, Na Sádkách 7, České Budějovice 370 05, Czech Republic
| | - Sara Soria-Píriz
- Département des sciences biologiques, Université du Québec à Montréal, 141 Av. du Président-Kennedy, Montréal, QC H2 × 1Y4, Montréal, QC, Canada
| | - Xinyu Sun
- Department of Fisheries and Wildlife, Michigan State University, East Lansing, MI 48824, USA
| | | | - Gesa A Weyhenmeyer
- Department of Ecology and Genetics/Limnology, Uppsala University, Norbyvägen 18D, 75236 Uppsala, Sweden
| | - Kiyoko Yokota
- Biology Department, State University of New York at Oneonta, Oneonta, NY 13820, USA
| | - Qing Zhan
- Department of Aquatic Ecology, Netherlands Institute of Ecology (NIOO-KNAW), P.O. Box 50, 6708 PB Wageningen, The Netherlands
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2
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Wierenga J, Thomas MK, Ranjan R, Ibelings BW. Complex effects of chytrid parasites on the growth of the cyanobacterium Planktothrix rubescens across interacting temperature and light gradients. ISME Commun 2022; 2:93. [PMID: 37938757 PMCID: PMC9723700 DOI: 10.1038/s43705-022-00178-5] [Citation(s) in RCA: 1] [Impact Index Per Article: 0.5] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Received: 03/02/2022] [Revised: 08/22/2022] [Accepted: 09/13/2022] [Indexed: 11/09/2023]
Abstract
Chytrids are important drivers of aquatic ecosystems as phytoplankton parasites. The interaction between these parasites and their hosts are shaped by abiotic factors such as temperature and light. Here, we performed a full-factorial experiment to study how temperature and light interact to affect the dynamics of the bloom-forming toxic cyanobacterium Planktothrix rubescens and its chytrid parasite. We used a dynamic host-parasite model to explore how temperature and light affect long term dynamics. At low temperatures, chytrids do not survive. Higher light and temperature levels stimulated both phytoplankton and chytrid growth, with complex effects on their dynamics. Model exploration indicates that increasing temperature and light shifts equilibrium outcomes from P. rubescens persisting alone to stable coexistence and then to limit cycles. This provides an alternative biological explanation for why P. rubescens is mainly found in the relatively cold and dark lake metalimnion - it may enable avoidance of its parasite. Our study emphasizes the importance of investigating how abiotic factors interact with biotic interactions to drive complex outcomes.
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Affiliation(s)
- Joren Wierenga
- Department F.A. Forel for Environmental and Aquatic Sciences and Institute for Environmental Sciences, University of Geneva, Geneva, Switzerland
| | - Mridul K Thomas
- Department F.A. Forel for Environmental and Aquatic Sciences and Institute for Environmental Sciences, University of Geneva, Geneva, Switzerland.
| | - Ravi Ranjan
- Helmholtz Institute of Functional Marine Biodiversity at the University of Oldenburg (HIFMB), Ammerländer Heerstraße 231, D-26129, Oldenburg, Germany
- Alfred-Wegener-Institute, Helmholtz-Centre for Polar and Marine Research (AWI), Am Handelshafen 12, 27570, Bremerhaven, Germany
| | - Bas W Ibelings
- Department F.A. Forel for Environmental and Aquatic Sciences and Institute for Environmental Sciences, University of Geneva, Geneva, Switzerland
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3
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Xiao M, Burford MA, Wood SA, Aubriot L, Ibelings BW, Prentice MJ, Galvanese EF, Harris TD, Hamilton DP. Schindler's legacy: from eutrophic lakes to the phosphorus utilization strategies of cyanobacteria. FEMS Microbiol Rev 2022; 46:6617595. [PMID: 35749580 PMCID: PMC9629505 DOI: 10.1093/femsre/fuac029] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [Track Full Text] [Download PDF] [Figures] [Journal Information] [Subscribe] [Scholar Register] [Received: 02/14/2022] [Revised: 06/01/2022] [Accepted: 06/22/2022] [Indexed: 01/09/2023] Open
Abstract
David Schindler and his colleagues pioneered studies in the 1970s on the role of phosphorus in stimulating cyanobacterial blooms in North American lakes. Our understanding of the nuances of phosphorus utilization by cyanobacteria has evolved since that time. We review the phosphorus utilization strategies used by cyanobacteria, such as use of organic forms, alternation between passive and active uptake, and luxury storage. While many aspects of physiological responses to phosphorus of cyanobacteria have been measured, our understanding of the critical processes that drive species diversity, adaptation and competition remains limited. We identify persistent critical knowledge gaps, particularly on the adaptation of cyanobacteria to low nutrient concentrations. We propose that traditional discipline-specific studies be adapted and expanded to encompass innovative new methodologies and take advantage of interdisciplinary opportunities among physiologists, molecular biologists, and modellers, to advance our understanding and prediction of toxic cyanobacteria, and ultimately to mitigate the occurrence of blooms.
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Affiliation(s)
- Man Xiao
- Corresponding author: Nanjing Institute of Geography & Limnology, Chinese Academy of Sciences, Nanjing, Jiangsu, China. E-mail:
| | - Michele A Burford
- Australian Rivers Institute, Griffith University, Nathan, QLD 4111, Australia
| | - Susanna A Wood
- Coastal and Freshwater Group, Cawthron Institute, Nelson, 7010, New Zealand
| | - Luis Aubriot
- Phytoplankton Physiology and Ecology Group, Sección Limnología, Instituto de Ecología y Ciencias Ambientales, Facultad de Ciencias; Universidad de la República, Montevideo, 11400, Uruguay
| | - Bas W Ibelings
- Department F.-A. Forel for Aquatic and Environmental Sciences and Institute for Environmental Sciences, University of Geneva, Geneva, 1290, Switzerland
| | - Matthew J Prentice
- Australian Rivers Institute, Griffith University, Nathan, QLD 4111, Australia
| | - Elena F Galvanese
- Laboratório de Análise e Síntese em Biodiversidade, Departamento de Botânica, Setor de Ciências Biológicas, Universidade Federal do Paraná, Curitiba-PR, 81531-998, Brazil,Programa de Pós-graduação em Ecologia e Conservação, Setor de Ciências Biológicas, Universidade Federal do Paraná, Curitiba-PR, 80060-140, Brazil
| | - Ted D Harris
- Kansas Biological Survey and Center for Ecological Research, Lawrence, KS, 66047, United States
| | - David P Hamilton
- Australian Rivers Institute, Griffith University, Nathan, QLD 4111, Australia
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4
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Stockwell JD, Doubek JP, Adrian R, Anneville O, Carey CC, Carvalho L, De Senerpont Domis LN, Dur G, Frassl MA, Grossart H, Ibelings BW, Lajeunesse MJ, Lewandowska AM, Llames ME, Matsuzaki SS, Nodine ER, Nõges P, Patil VP, Pomati F, Rinke K, Rudstam LG, Rusak JA, Salmaso N, Seltmann CT, Straile D, Thackeray SJ, Thiery W, Urrutia‐Cordero P, Venail P, Verburg P, Woolway RI, Zohary T, Andersen MR, Bhattacharya R, Hejzlar J, Janatian N, Kpodonu ATNK, Williamson TJ, Wilson HL. Storm impacts on phytoplankton community dynamics in lakes. Glob Chang Biol 2020; 26:2756-2784. [PMID: 32133744 PMCID: PMC7216882 DOI: 10.1111/gcb.15033] [Citation(s) in RCA: 60] [Impact Index Per Article: 15.0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [MESH Headings] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Received: 07/18/2019] [Accepted: 01/25/2020] [Indexed: 05/03/2023]
Abstract
In many regions across the globe, extreme weather events such as storms have increased in frequency, intensity, and duration due to climate change. Ecological theory predicts that such extreme events should have large impacts on ecosystem structure and function. High winds and precipitation associated with storms can affect lakes via short-term runoff events from watersheds and physical mixing of the water column. In addition, lakes connected to rivers and streams will also experience flushing due to high flow rates. Although we have a well-developed understanding of how wind and precipitation events can alter lake physical processes and some aspects of biogeochemical cycling, our mechanistic understanding of the emergent responses of phytoplankton communities is poor. Here we provide a comprehensive synthesis that identifies how storms interact with lake and watershed attributes and their antecedent conditions to generate changes in lake physical and chemical environments. Such changes can restructure phytoplankton communities and their dynamics, as well as result in altered ecological function (e.g., carbon, nutrient and energy cycling) in the short- and long-term. We summarize the current understanding of storm-induced phytoplankton dynamics, identify knowledge gaps with a systematic review of the literature, and suggest future research directions across a gradient of lake types and environmental conditions.
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Affiliation(s)
- Evanthia Mantzouki
- Department F.-A. Forel for Environmental and Aquatic Sciences, University of Geneva, Geneva, Switzerland
| | - Bas W. Ibelings
- Department F.-A. Forel for Environmental and Aquatic Sciences, University of Geneva, Geneva, Switzerland
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6
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Mantzouki E, Lürling M, Fastner J, de Senerpont Domis L, Wilk-Woźniak E, Koreivienė J, Seelen L, Teurlincx S, Verstijnen Y, Krztoń W, Walusiak E, Karosienė J, Kasperovičienė J, Savadova K, Vitonytė I, Cillero-Castro C, Budzyńska A, Goldyn R, Kozak A, Rosińska J, Szeląg-Wasielewska E, Domek P, Jakubowska-Krepska N, Kwasizur K, Messyasz B, Pełechaty A, Pełechaty M, Kokocinski M, García-Murcia A, Real M, Romans E, Noguero-Ribes J, Duque DP, Fernández-Morán E, Karakaya N, Häggqvist K, Demir N, Beklioğlu M, Filiz N, Levi EE, Iskin U, Bezirci G, Tavşanoğlu ÜN, Özhan K, Gkelis S, Panou M, Fakioglu Ö, Avagianos C, Kaloudis T, Çelik K, Yilmaz M, Marcé R, Catalán N, Bravo AG, Buck M, Colom-Montero W, Mustonen K, Pierson D, Yang Y, Raposeiro PM, Gonçalves V, Antoniou MG, Tsiarta N, McCarthy V, Perello VC, Feldmann T, Laas A, Panksep K, Tuvikene L, Gagala I, Mankiewicz-Boczek J, Yağcı MA, Çınar Ş, Çapkın K, Yağcı A, Cesur M, Bilgin F, Bulut C, Uysal R, Obertegger U, Boscaini A, Flaim G, Salmaso N, Cerasino L, Richardson J, Visser PM, Verspagen JMH, Karan T, Soylu EN, Maraşlıoğlu F, Napiórkowska-Krzebietke A, Ochocka A, Pasztaleniec A, Antão-Geraldes AM, Vasconcelos V, Morais J, Vale M, Köker L, Akçaalan R, Albay M, Špoljarić Maronić D, Stević F, Žuna Pfeiffer T, Fonvielle J, Straile D, Rothhaupt KO, Hansson LA, Urrutia-Cordero P, Bláha L, Geriš R, Fránková M, Koçer MAT, Alp MT, Remec-Rekar S, Elersek T, Triantis T, Zervou SK, Hiskia A, Haande S, Skjelbred B, Madrecka B, Nemova H, Drastichova I, Chomova L, Edwards C, Sevindik TO, Tunca H, Önem B, Aleksovski B, Krstić S, Vucelić IB, Nawrocka L, Salmi P, Machado-Vieira D, de Oliveira AG, Delgado-Martín J, García D, Cereijo JL, Gomà J, Trapote MC, Vegas-Vilarrúbia T, Obrador B, Grabowska M, Karpowicz M, Chmura D, Úbeda B, Gálvez JÁ, Özen A, Christoffersen KS, Warming TP, Kobos J, Mazur-Marzec H, Pérez-Martínez C, Ramos-Rodríguez E, Arvola L, Alcaraz-Párraga P, Toporowska M, Pawlik-Skowronska B, Niedźwiecki M, Pęczuła W, Leira M, Hernández A, Moreno-Ostos E, Blanco JM, Rodríguez V, Montes-Pérez JJ, Palomino RL, Rodríguez-Pérez E, Carballeira R, Camacho A, Picazo A, Rochera C, Santamans AC, Ferriol C, Romo S, Soria JM, Dunalska J, Sieńska J, Szymański D, Kruk M, Kostrzewska-Szlakowska I, Jasser I, Žutinić P, Gligora Udovič M, Plenković-Moraj A, Frąk M, Bańkowska-Sobczak A, Wasilewicz M, Özkan K, Maliaka V, Kangro K, Grossart HP, Paerl HW, Carey CC, Ibelings BW. Temperature Effects Explain Continental Scale Distribution of Cyanobacterial Toxins. Toxins (Basel) 2018; 10:toxins10040156. [PMID: 29652856 PMCID: PMC5923322 DOI: 10.3390/toxins10040156] [Citation(s) in RCA: 97] [Impact Index Per Article: 16.2] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Download PDF] [Figures] [Journal Information] [Subscribe] [Scholar Register] [Received: 02/15/2018] [Revised: 03/27/2018] [Accepted: 03/29/2018] [Indexed: 11/29/2022] Open
Abstract
Insight into how environmental change determines the production and distribution of cyanobacterial toxins is necessary for risk assessment. Management guidelines currently focus on hepatotoxins (microcystins). Increasing attention is given to other classes, such as neurotoxins (e.g., anatoxin-a) and cytotoxins (e.g., cylindrospermopsin) due to their potency. Most studies examine the relationship between individual toxin variants and environmental factors, such as nutrients, temperature and light. In summer 2015, we collected samples across Europe to investigate the effect of nutrient and temperature gradients on the variability of toxin production at a continental scale. Direct and indirect effects of temperature were the main drivers of the spatial distribution in the toxins produced by the cyanobacterial community, the toxin concentrations and toxin quota. Generalized linear models showed that a Toxin Diversity Index (TDI) increased with latitude, while it decreased with water stability. Increases in TDI were explained through a significant increase in toxin variants such as MC-YR, anatoxin and cylindrospermopsin, accompanied by a decreasing presence of MC-LR. While global warming continues, the direct and indirect effects of increased lake temperatures will drive changes in the distribution of cyanobacterial toxins in Europe, potentially promoting selection of a few highly toxic species or strains.
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Affiliation(s)
- Evanthia Mantzouki
- Department F.-A. Forel for Environmental and Aquatic Sciences, University of Geneva, 1205 Geneva, Switzerland.
| | - Miquel Lürling
- Department of Environmental Sciences, Wageningen University & Research, 6700 Wageningen, The Netherlands.
- Department of Aquatic Ecology, Netherlands Institute of Ecology (NIOO-KNAW), 6700 Wageningen, The Netherlands.
| | - Jutta Fastner
- German Environment Agency, Unit Drinking Water Resources and Water Treatment, Corrensplatz 1, 14195 Berlin, Germany.
| | - Lisette de Senerpont Domis
- Department of Environmental Sciences, Wageningen University & Research, 6700 Wageningen, The Netherlands.
- Department of Aquatic Ecology, Netherlands Institute of Ecology (NIOO-KNAW), 6700 Wageningen, The Netherlands.
| | - Elżbieta Wilk-Woźniak
- Institute of Nature Conservation, Polish Academy of Sciences, 31-120 Krakow, Poland.
| | - Judita Koreivienė
- Institute of Botany, Nature Research Centre, Vilnius 08412, Lithuania.
| | - Laura Seelen
- Department of Environmental Sciences, Wageningen University & Research, 6700 Wageningen, The Netherlands.
- Department of Aquatic Ecology, Netherlands Institute of Ecology (NIOO-KNAW), 6700 Wageningen, The Netherlands.
| | - Sven Teurlincx
- Department of Aquatic Ecology, Netherlands Institute of Ecology (NIOO-KNAW), 6700 Wageningen, The Netherlands.
| | - Yvon Verstijnen
- Department of Environmental Sciences, Wageningen University & Research, 6700 Wageningen, The Netherlands.
| | - Wojciech Krztoń
- Institute of Nature Conservation, Polish Academy of Sciences, 31-120 Krakow, Poland.
| | - Edward Walusiak
- Institute of Nature Conservation, Polish Academy of Sciences, 31-120 Krakow, Poland.
| | - Jūratė Karosienė
- Institute of Botany, Nature Research Centre, Vilnius 08412, Lithuania.
| | | | - Ksenija Savadova
- Institute of Botany, Nature Research Centre, Vilnius 08412, Lithuania.
| | - Irma Vitonytė
- Institute of Botany, Nature Research Centre, Vilnius 08412, Lithuania.
| | | | - Agnieszka Budzyńska
- Department ofWater Protection, Adam Mickiewicz University, 61614 Poznan, Poland.
| | - Ryszard Goldyn
- Department ofWater Protection, Adam Mickiewicz University, 61614 Poznan, Poland.
| | - Anna Kozak
- Department ofWater Protection, Adam Mickiewicz University, 61614 Poznan, Poland.
| | - Joanna Rosińska
- Department ofWater Protection, Adam Mickiewicz University, 61614 Poznan, Poland.
| | | | - Piotr Domek
- Department ofWater Protection, Adam Mickiewicz University, 61614 Poznan, Poland.
| | | | - Kinga Kwasizur
- Department of Hydrobiology, Adam Mickiewicz University, 61614 Poznan, Poland.
| | - Beata Messyasz
- Department of Hydrobiology, Adam Mickiewicz University, 61614 Poznan, Poland.
| | | | - Mariusz Pełechaty
- Department of Hydrobiology, Adam Mickiewicz University, 61614 Poznan, Poland.
| | - Mikolaj Kokocinski
- Department of Hydrobiology, Adam Mickiewicz University, 61614 Poznan, Poland.
| | - Ana García-Murcia
- Department of Limnology and Water Quality, AECOM U.R.S, 08036 Barcelona, Spain.
| | - Monserrat Real
- Department of Limnology and Water Quality, AECOM U.R.S, 08036 Barcelona, Spain.
| | - Elvira Romans
- Department of Limnology and Water Quality, AECOM U.R.S, 08036 Barcelona, Spain.
| | - Jordi Noguero-Ribes
- Department of Limnology and Water Quality, AECOM U.R.S, 08036 Barcelona, Spain.
| | - David Parreño Duque
- Department of Limnology and Water Quality, AECOM U.R.S, 08036 Barcelona, Spain.
| | | | - Nusret Karakaya
- Department of Environmental Engineering, Abant Izzet Baysal University, 14280 Bolu, Turkey.
| | - Kerstin Häggqvist
- Department of Science and Engineering, Åbo Akademi University, 20520 Åbo, Finland.
| | - Nilsun Demir
- Department of Fisheries and Aquaculture, Ankara University, 6100 Ankara, Turkey.
| | - Meryem Beklioğlu
- Department of biology, Middle East Technical University, 6800 Ankara, Turkey.
| | - Nur Filiz
- Department of biology, Middle East Technical University, 6800 Ankara, Turkey.
| | - Eti E. Levi
- Department of biology, Middle East Technical University, 6800 Ankara, Turkey.
| | - Uğur Iskin
- Department of biology, Middle East Technical University, 6800 Ankara, Turkey.
| | - Gizem Bezirci
- Department of biology, Middle East Technical University, 6800 Ankara, Turkey.
| | | | - Koray Özhan
- Institute of Marine Sciences, Department of Oceanography, Middle East Technical University, 06800 Ankara, Turkey.
| | - Spyros Gkelis
- Department of Botany, Aristotle University of Thessaloniki, 54124 Thessaloniki, Greece.
| | - Manthos Panou
- Department of Botany, Aristotle University of Thessaloniki, 54124 Thessaloniki, Greece.
| | - Özden Fakioglu
- Department of Basic Science, Ataturk University, 25240 Erzurum, Turkey.
| | - Christos Avagianos
- Water Quality Department, Athens Water Supply and Sewerage Company, 11146 Athens, Greece.
| | - Triantafyllos Kaloudis
- Water Quality Department, Athens Water Supply and Sewerage Company, 11146 Athens, Greece.
| | - Kemal Çelik
- Department of Biology, Balikesir University, 10145 Balikesir, Turkey.
| | - Mete Yilmaz
- Department of Bioengineering, Bursa Technical University, 16310 Bursa, Turkey.
| | - Rafael Marcé
- Catalan Institute for Water Research (ICRA), 17003 Girona, Spain.
| | - Nuria Catalán
- Catalan Institute for Water Research (ICRA), 17003 Girona, Spain.
- Department of Ecology and Genetics, Limnology, Uppsala University, 75236 Uppsala, Sweden.
| | - Andrea G. Bravo
- Department of Ecology and Genetics, Limnology, Uppsala University, 75236 Uppsala, Sweden.
| | - Moritz Buck
- Department of Ecology and Genetics, Limnology, Uppsala University, 75236 Uppsala, Sweden.
| | - William Colom-Montero
- Department of Ecology and Genetics, Erken Laboratory, Uppsala University, 76173 Norrtalje, Sweden.
| | - Kristiina Mustonen
- Department of Ecology and Genetics, Erken Laboratory, Uppsala University, 76173 Norrtalje, Sweden.
| | - Don Pierson
- Department of Ecology and Genetics, Erken Laboratory, Uppsala University, 76173 Norrtalje, Sweden.
| | - Yang Yang
- Department of Ecology and Genetics, Erken Laboratory, Uppsala University, 76173 Norrtalje, Sweden.
| | - Pedro M. Raposeiro
- Research Center in Biodiversity and Genetic Resources (CIBIO-Azores), InBIO Associated Laboratory, Faculty of Sciences and Technology, University of the Azores, 9501-801 Ponta Delgada, Portugal.
| | - Vítor Gonçalves
- Research Center in Biodiversity and Genetic Resources (CIBIO-Azores), InBIO Associated Laboratory, Faculty of Sciences and Technology, University of the Azores, 9501-801 Ponta Delgada, Portugal.
| | - Maria G. Antoniou
- Department of Environmental Science and Technology, Cyprus University of Technology, 3036 Lemesos, Cyprus.
| | - Nikoletta Tsiarta
- Department of Environmental Science and Technology, Cyprus University of Technology, 3036 Lemesos, Cyprus.
| | - Valerie McCarthy
- Centre for Freshwater and Environmental Studies, Dundalk Institute of Technology, A91 K584 Dundalk, Ireland.
| | - Victor C. Perello
- Centre for Freshwater and Environmental Studies, Dundalk Institute of Technology, A91 K584 Dundalk, Ireland.
| | - Tõnu Feldmann
- Institute of Agricultural and Environmental Sciences, Estonian University of Life Sciences, 51014 Tartu, Estonia.
| | - Alo Laas
- Institute of Agricultural and Environmental Sciences, Estonian University of Life Sciences, 51014 Tartu, Estonia.
| | - Kristel Panksep
- Institute of Agricultural and Environmental Sciences, Estonian University of Life Sciences, 51014 Tartu, Estonia.
| | - Lea Tuvikene
- Institute of Agricultural and Environmental Sciences, Estonian University of Life Sciences, 51014 Tartu, Estonia.
| | - Ilona Gagala
- European Regional Centre for Ecohydrology of the Polish Academy of Sciences, 90364 Lodz, Poland.
| | - Joana Mankiewicz-Boczek
- European Regional Centre for Ecohydrology of the Polish Academy of Sciences, 90364 Lodz, Poland.
| | - Meral Apaydın Yağcı
- Republic of Turkey Ministry of Food Agriculture, Fisheries Research Institute, 32500 Eğirdir, Isparta, Turkey.
| | - Şakir Çınar
- Republic of Turkey Ministry of Food Agriculture, Fisheries Research Institute, 32500 Eğirdir, Isparta, Turkey.
| | - Kadir Çapkın
- Republic of Turkey Ministry of Food Agriculture, Fisheries Research Institute, 32500 Eğirdir, Isparta, Turkey.
| | - Abdulkadir Yağcı
- Republic of Turkey Ministry of Food Agriculture, Fisheries Research Institute, 32500 Eğirdir, Isparta, Turkey.
| | - Mehmet Cesur
- Republic of Turkey Ministry of Food Agriculture, Fisheries Research Institute, 32500 Eğirdir, Isparta, Turkey.
| | - Fuat Bilgin
- Republic of Turkey Ministry of Food Agriculture, Fisheries Research Institute, 32500 Eğirdir, Isparta, Turkey.
| | - Cafer Bulut
- Republic of Turkey Ministry of Food Agriculture, Fisheries Research Institute, 32500 Eğirdir, Isparta, Turkey.
| | - Rahmi Uysal
- Republic of Turkey Ministry of Food Agriculture, Fisheries Research Institute, 32500 Eğirdir, Isparta, Turkey.
| | - Ulrike Obertegger
- Department of Sustainable Ecosystems and Bioresources, Fondazione Edmund Mach, 38010 San Michele all’Adige, Italy.
| | - Adriano Boscaini
- Department of Sustainable Ecosystems and Bioresources, Fondazione Edmund Mach, 38010 San Michele all’Adige, Italy.
| | - Giovanna Flaim
- Department of Sustainable Ecosystems and Bioresources, Fondazione Edmund Mach, 38010 San Michele all’Adige, Italy.
| | - Nico Salmaso
- Department of Sustainable Ecosystems and Bioresources, Fondazione Edmund Mach, 38010 San Michele all’Adige, Italy.
| | - Leonardo Cerasino
- Department of Sustainable Ecosystems and Bioresources, Fondazione Edmund Mach, 38010 San Michele all’Adige, Italy.
| | - Jessica Richardson
- Department of Biological and Environmental Sciences, University of Stirling, Stirling FK9 4LA, UK.
| | - Petra M. Visser
- Department of Freshwater and Marine Ecology, University of Amsterdam, 1090 GE Amsterdam, The Netherlands.
| | - Jolanda M. H. Verspagen
- Department of Freshwater and Marine Ecology, University of Amsterdam, 1090 GE Amsterdam, The Netherlands.
| | - Tünay Karan
- Department of Molecular Biology and Genetics, Gaziosmanpasa University, 60250 Merkez, Turkey.
| | | | | | | | - Agnieszka Ochocka
- Department of Freshwater Protection, Institute of Environmental Protection- National Research Institute, 01-692 Warsaw, Poland.
| | - Agnieszka Pasztaleniec
- Department of Freshwater Protection, Institute of Environmental Protection- National Research Institute, 01-692 Warsaw, Poland.
| | - Ana M. Antão-Geraldes
- Centro de Investigação da Montanha, Instituto Politécnico de Bragança, Campus de Santa Apolónia, 5300-253 Bragança, Portugal;
| | - Vitor Vasconcelos
- Interdisciplinary Centre of Marine and Environmental Research (CIIMAR) and University of Porto, 4450-208 Matosinhos, Portugal.
| | - João Morais
- Interdisciplinary Centre of Marine and Environmental Research (CIIMAR) and University of Porto, 4450-208 Matosinhos, Portugal.
| | - Micaela Vale
- Interdisciplinary Centre of Marine and Environmental Research (CIIMAR) and University of Porto, 4450-208 Matosinhos, Portugal.
| | - Latife Köker
- Department of Freshwater Resource and Management, Faculty of Aquatic Sciences, Istanbul University, 34134 Istanbul, Turkey.
| | - Reyhan Akçaalan
- Department of Freshwater Resource and Management, Faculty of Aquatic Sciences, Istanbul University, 34134 Istanbul, Turkey.
| | - Meriç Albay
- Department of Freshwater Resource and Management, Faculty of Aquatic Sciences, Istanbul University, 34134 Istanbul, Turkey.
| | | | - Filip Stević
- Department of Biology, Josip Juraj Strossmayer University of Osijek, 31000 Osijek, Croatia.
| | - Tanja Žuna Pfeiffer
- Department of Biology, Josip Juraj Strossmayer University of Osijek, 31000 Osijek, Croatia.
| | - Jeremy Fonvielle
- Department of Experimental Limnology, Leibniz Institute of Freshwater Ecology and Inland Fisheries, 16775 Stechlin, Germany.
| | - Dietmar Straile
- Department of Biology, Limnological Institute, University of Konstanz, 78464 Konstanz, Germany.
| | - Karl-Otto Rothhaupt
- Department of Biology, Limnological Institute, University of Konstanz, 78464 Konstanz, Germany.
| | | | - Pablo Urrutia-Cordero
- Department of Ecology and Genetics, Limnology, Uppsala University, 75236 Uppsala, Sweden.
- Department of Biology, Lund University, 22362 Lund, Sweden.
| | - Luděk Bláha
- RECETOX, Faculty of Science, Masaryk University, 62500 Brno, Czech Republic.
| | - Rodan Geriš
- Department of Hydrobiology, Morava Board Authority, 60200 Brno, Czech Republic.
| | - Markéta Fránková
- Laboratory of Paleoecology, Institute of Botany, The Czech Academy of Sciences, 60200 Brno, Czech Republic.
| | - Mehmet Ali Turan Koçer
- Department of Environment and Resource Management, Mediterranean Fisheries Research Production and Training Institute, 7090 Antalya, Turkey.
| | - Mehmet Tahir Alp
- Faculty of Aquaculture, Mersin University, 33160 Mersin, Turkey.
| | - Spela Remec-Rekar
- Department ofWater Quality, Slovenian Environmental Agency, 1000 Ljubljana, Slovenia.
| | - Tina Elersek
- Department of Genetic Toxicology and Cancer Biology, National Institute of Biology, 1000 Ljubljana, Slovenia.
| | - Theodoros Triantis
- Institute of Nanoscience and Nanotechnology, National Center for Scientific Research «DEMOKRITOS», 15341 Attiki, Greece.
| | - Sevasti-Kiriaki Zervou
- Institute of Nanoscience and Nanotechnology, National Center for Scientific Research «DEMOKRITOS», 15341 Attiki, Greece.
| | - Anastasia Hiskia
- Institute of Nanoscience and Nanotechnology, National Center for Scientific Research «DEMOKRITOS», 15341 Attiki, Greece.
| | - Sigrid Haande
- Department of Freshwater Ecology, Norwegian Institute for Water Research, 0349 Oslo, Norway.
| | - Birger Skjelbred
- Department of Freshwater Ecology, Norwegian Institute for Water Research, 0349 Oslo, Norway.
| | - Beata Madrecka
- Institute of Environmental Engineering, Poznan University of Technology, 60965 Poznan, Poland.
| | - Hana Nemova
- National Reference Center for Hydrobiology, Public Health Authority of the Slovak Republic, 82645 Bratislava, Slovakia.
| | - Iveta Drastichova
- National Reference Center for Hydrobiology, Public Health Authority of the Slovak Republic, 82645 Bratislava, Slovakia.
| | - Lucia Chomova
- National Reference Center for Hydrobiology, Public Health Authority of the Slovak Republic, 82645 Bratislava, Slovakia.
| | - Christine Edwards
- School of Pharmacy and Life Sciences, Robert Gordon University, Aberdeen AB10 7GJ, UK.
| | | | - Hatice Tunca
- Department of Biology, Sakarya University, 54187 Sakarya, Turkey.
| | - Burçin Önem
- Department of Biology, Sakarya University, 54187 Sakarya, Turkey.
| | - Boris Aleksovski
- Faculty of Natural Sciences and Mathematics, SS Cyril and Methodius University, 1000 Skopje, Macedonia.
| | - Svetislav Krstić
- Faculty of Natural Sciences and Mathematics, SS Cyril and Methodius University, 1000 Skopje, Macedonia.
| | - Itana Bokan Vucelić
- Department for Ecotoxicology, Teaching Institute of Public Health of Primorje-Gorski Kotar County, 51000 Rijeka, Croatia.
| | - Lidia Nawrocka
- Institute of Technology, The State University of Applied Sciences, 82300 Elblag, Poland.
| | - Pauliina Salmi
- Department of Biological and Environmental Science, University of Jyväskylä, 40014 Jyväskylä, Finland.
| | - Danielle Machado-Vieira
- Departamento de Sistemática e Ecologia, Universidade Federal da Paraíba, 58059-970 Paraíba, Brasil.
| | | | | | - David García
- Department of Civil Engineering, University of A Coruña, 15192 A Coruña, Spain.
| | - Jose Luís Cereijo
- Department of Civil Engineering, University of A Coruña, 15192 A Coruña, Spain.
| | - Joan Gomà
- Department of Evolutionary Biology, Ecology, and Environmental Sciences, University of Barcelona, 08028 Barcelona, Spain.
| | - Mari Carmen Trapote
- Department of Evolutionary Biology, Ecology, and Environmental Sciences, University of Barcelona, 08028 Barcelona, Spain.
| | - Teresa Vegas-Vilarrúbia
- Department of Evolutionary Biology, Ecology, and Environmental Sciences, University of Barcelona, 08028 Barcelona, Spain.
| | - Biel Obrador
- Department of Evolutionary Biology, Ecology, and Environmental Sciences, University of Barcelona, 08028 Barcelona, Spain.
| | - Magdalena Grabowska
- Department of Hydrobiology, University of Bialystok, 15245 Bialystok, Poland.
| | - Maciej Karpowicz
- Department of Hydrobiology, University of Bialystok, 15245 Bialystok, Poland.
| | - Damian Chmura
- Institute of Environmental Protection and Engineering, University of Bielsko-Biala, 43309 Bielsko-Biala, Poland.
| | - Bárbara Úbeda
- Department of Biology, University of Cádiz, 11510 Puerto Real, Cádiz, Spain.
| | - José Ángel Gálvez
- Department of Biology, University of Cádiz, 11510 Puerto Real, Cádiz, Spain.
| | - Arda Özen
- Department of Forest Engineering, University of Cankiri Karatekin, 18200 Cankiri, Turkey.
| | | | - Trine Perlt Warming
- Freshwater Biological Laboratory, Department of Biology, University of Copenhagen, 2100 Copenhagen, Denmark.
| | - Justyna Kobos
- Department of Marine Biotechnology, University of Gdansk, 81378 Gdynia, Poland.
| | - Hanna Mazur-Marzec
- Department of Marine Biotechnology, University of Gdansk, 81378 Gdynia, Poland.
| | | | | | - Lauri Arvola
- Lammi Biological Station, University of Helsinki, 16900 Lammi, Finland.
| | - Pablo Alcaraz-Párraga
- Department of Animal Biology, Plant Biology and Ecology, University of Jaen, 23701 Jaen, Spain.
| | - Magdalena Toporowska
- Department of Hydrobiology and Protection of Ecosystems, University of Life Sciences in Lublin, 20262 Lublin, Poland.
| | - Barbara Pawlik-Skowronska
- Department of Hydrobiology and Protection of Ecosystems, University of Life Sciences in Lublin, 20262 Lublin, Poland.
| | - Michał Niedźwiecki
- Department of Hydrobiology and Protection of Ecosystems, University of Life Sciences in Lublin, 20262 Lublin, Poland.
| | - Wojciech Pęczuła
- Department of Hydrobiology and Protection of Ecosystems, University of Life Sciences in Lublin, 20262 Lublin, Poland.
| | - Manel Leira
- Instituto Dom Luiz, University of Lisbon, 1749016 Lisbon, Portugal.
| | - Armand Hernández
- Institute of Earth Sciences Jaume Almera, ICTJA, CSIC, 08028 Barcelona, Spain.
| | | | | | | | | | | | | | - Rafael Carballeira
- Centro de Investigacións Cientificas Avanzadas (CICA), Facultade de Ciencias, Universidade da Coruña, 15071 A Coruña, Spain.
| | - Antonio Camacho
- Cavanilles Institute of Biodiversity and Evolutionary Biology, University of Valencia, 46980 Paterna Valencia, Spain.
| | - Antonio Picazo
- Cavanilles Institute of Biodiversity and Evolutionary Biology, University of Valencia, 46980 Paterna Valencia, Spain.
| | - Carlos Rochera
- Cavanilles Institute of Biodiversity and Evolutionary Biology, University of Valencia, 46980 Paterna Valencia, Spain.
| | - Anna C. Santamans
- Cavanilles Institute of Biodiversity and Evolutionary Biology, University of Valencia, 46980 Paterna Valencia, Spain.
| | - Carmen Ferriol
- Cavanilles Institute of Biodiversity and Evolutionary Biology, University of Valencia, 46980 Paterna Valencia, Spain.
| | - Susana Romo
- Department of Microbiology and Ecology, University of Valencia, 46100 Burjassot, Spain.
| | - Juan Miguel Soria
- Department of Microbiology and Ecology, University of Valencia, 46100 Burjassot, Spain. (J.M.S.)
| | - Julita Dunalska
- Department ofWater Protection Engineering, University ofWarmia and Mazury, 10-720 Olsztyn, Poland.
| | - Justyna Sieńska
- Department ofWater Protection Engineering, University ofWarmia and Mazury, 10-720 Olsztyn, Poland.
| | - Daniel Szymański
- Department ofWater Protection Engineering, University ofWarmia and Mazury, 10-720 Olsztyn, Poland.
| | - Marek Kruk
- Department of Tourism, Recreation and Ecology, University of Warmia and Mazury, 10-720 Olsztyn, Poland.
| | | | - Iwona Jasser
- Department of Plant Ecology and Environmental Conservation, Faculty of Biology, University ofWarsaw, 02-089 Warsaw, Poland.
| | - Petar Žutinić
- Department of Biology, Faculty of Science, University of Zagreb, 10000 Zagreb, Croatia.
| | - Marija Gligora Udovič
- Department of Biology, Faculty of Science, University of Zagreb, 10000 Zagreb, Croatia.
| | | | - Magdalena Frąk
- Department of Environmental Improvement, Faculty of Civil and Environmental Engineering, Warsaw University of Life Sciences—SGGW, 02-787Warsaw, Poland.
| | - Agnieszka Bańkowska-Sobczak
- Department of Hydraulic Engineering, Faculty of Civil and Environmental Engineering, Warsaw University of Life Sciences—SGGW, 02-787Warsaw, Poland.
| | - Michał Wasilewicz
- Department of Hydraulic Engineering, Faculty of Civil and Environmental Engineering, Warsaw University of Life Sciences—SGGW, 02-787Warsaw, Poland.
| | - Korhan Özkan
- Institute of Marine Sciences, Marine Biology and Fisheries, Middle East Technical University, 06800 Ankara, Turkey.
| | - Valentini Maliaka
- Society for the Protection of Prespa, 53077 Agios Germanos, Greece.
- Institute for Water and Wetland Research, Department of Aquatic Ecology and Environmental Biology, Radboud University Nijmegen, 6525 AJ Nijmegen, The Netherlands.
- Department of Environmental Sciences, Wageningen University & Research, 6700 Wageningen, The Netherlands.
| | - Kersti Kangro
- Institute of Agricultural and Environmental Sciences, Estonian University of Life Sciences, 51014 Tartu, Estonia.
- Tartu Observatory, Faculty of Science and Technology, University of Tartu, 61602 Tartu, Estonia.
| | - Hans-Peter Grossart
- Department of Experimental Limnology, Leibniz Institute of Freshwater Ecology and Inland Fisheries, 16775 Stechlin, Germany.
- Institute of Biochemistry and Biology, Potsdam University, 14469 Potsdam, Germany.
| | - Hans W. Paerl
- Institute of Marine Sciences, University of North Carolina at Chapel Hill, Chapel Hill, NC 28557, USA.
| | - Cayelan C. Carey
- Department of Biological Sciences, Virginia Tech, Blacksburg, VA 24061, USA.
| | - Bas W. Ibelings
- Department F.-A. Forel for Environmental and Aquatic Sciences, University of Geneva, 1205 Geneva, Switzerland.
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7
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Frenken T, Alacid E, Berger SA, Bourne EC, Gerphagnon M, Grossart HP, Gsell AS, Ibelings BW, Kagami M, Küpper FC, Letcher PM, Loyau A, Miki T, Nejstgaard JC, Rasconi S, Reñé A, Rohrlack T, Rojas-Jimenez K, Schmeller DS, Scholz B, Seto K, Sime-Ngando T, Sukenik A, Van de Waal DB, Van den Wyngaert S, Van Donk E, Wolinska J, Wurzbacher C, Agha R. Integrating chytrid fungal parasites into plankton ecology: research gaps and needs. Environ Microbiol 2017; 19:3802-3822. [DOI: 10.1111/1462-2920.13827] [Citation(s) in RCA: 120] [Impact Index Per Article: 17.1] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 03/20/2017] [Revised: 06/09/2017] [Accepted: 06/10/2017] [Indexed: 01/19/2023]
Affiliation(s)
- Thijs Frenken
- Department of Aquatic Ecology; Netherlands Institute of Ecology (NIOO-KNAW), Droevendaalsesteeg 10; Wageningen PB 6708 The Netherlands
| | - Elisabet Alacid
- Departament de Biologia Marina i Oceanografia; Institut de Ciències del Mar (CSIC), Pg. Marítim de la Barceloneta, 37-49; Barcelona 08003 Spain
| | - Stella A. Berger
- Department of Experimental Limnology; Leibniz-Institute of Freshwater Ecology and Inland Fisheries (IGB), Alte Fischerhuette 2; Stechlin D-16775 Germany
| | - Elizabeth C. Bourne
- Berlin Center for Genomics in Biodiversity Research, Königin-Luise-Straβe 6-8; Berlin D-14195 Germany
- Department of Ecosystem Research; Leibniz-Institute of Freshwater Ecology and Inland Fisheries (IGB), Müggelseedamm 301; Berlin 12587 Germany
| | - Mélanie Gerphagnon
- Department of Ecosystem Research; Leibniz-Institute of Freshwater Ecology and Inland Fisheries (IGB), Müggelseedamm 301; Berlin 12587 Germany
| | - Hans-Peter Grossart
- Department of Experimental Limnology; Leibniz-Institute of Freshwater Ecology and Inland Fisheries (IGB), Alte Fischerhuette 2; Stechlin D-16775 Germany
- Institute for Biochemistry and Biology, Potsdam University, Maulbeerallee 2; Potsdam D-14476 Germany
| | - Alena S. Gsell
- Department of Aquatic Ecology; Netherlands Institute of Ecology (NIOO-KNAW), Droevendaalsesteeg 10; Wageningen PB 6708 The Netherlands
| | - Bas W. Ibelings
- Department F.-A. Forel for Environmental and Aquatic Sciences & Institute for Environmental Sciences; University of Geneva, 66 Boulevard Carl Vogt; Geneva 4 CH 1211 Switzerland
| | - Maiko Kagami
- Department of Environmental Sciences, Faculty of Science; Toho University, 2-2-1, Miyama; Funabashi Chiba 274-8510 Japan
| | - Frithjof C. Küpper
- Oceanlab, University of Aberdeen, Main Street; Newburgh Scotland AB41 6AA UK
| | - Peter M. Letcher
- Department of Biological Sciences; The University of Alabama, 300 Hackberry Lane; Tuscaloosa AL 35487 USA
| | - Adeline Loyau
- Department of System Ecotoxicology; Helmholtz Center for Environmental Research - UFZ, Permoserstrasse 15; 04318 Leipzig Germany
- Department of Conservation Biology; Helmholtz Center for Environmental Research - UFZ, Permoserstrasse 15; Leipzig 04318 Germany
- ECOLAB, Université de Toulouse, CNRS, INPT, UPS; Toulouse France
| | - Takeshi Miki
- Institute of Oceanography; National Taiwan University, No.1 Section 4, Roosevelt Road; Taipei 10617 Taiwan
- Research Center for Environmental Changes; Academia Sinica, No.128 Section 2, Academia Road, Nankang; Taipei 11529 Taiwan
| | - Jens C. Nejstgaard
- Department of Experimental Limnology; Leibniz-Institute of Freshwater Ecology and Inland Fisheries (IGB), Alte Fischerhuette 2; Stechlin D-16775 Germany
| | - Serena Rasconi
- WasserCluster Lunz - Biological Station; Inter-University Centre for Aquatic Ecosystem Research, A-3293 Lunz am See; Austria
| | - Albert Reñé
- Departament de Biologia Marina i Oceanografia; Institut de Ciències del Mar (CSIC), Pg. Marítim de la Barceloneta, 37-49; Barcelona 08003 Spain
| | - Thomas Rohrlack
- Faculty of Environmental Sciences and Natural Resource Management; Norwegian University of Life Sciences, P.O. Box 5003, NO-1432, Ås; Norway
| | - Keilor Rojas-Jimenez
- Department of Experimental Limnology; Leibniz-Institute of Freshwater Ecology and Inland Fisheries (IGB), Alte Fischerhuette 2; Stechlin D-16775 Germany
- Universidad Latina de Costa Rica, Campus San Pedro, Apdo; San Jose 10138-1000 Costa Rica
| | - Dirk S. Schmeller
- Department of Conservation Biology; Helmholtz Center for Environmental Research - UFZ, Permoserstrasse 15; Leipzig 04318 Germany
- ECOLAB, Université de Toulouse, CNRS, INPT, UPS; Toulouse France
| | - Bettina Scholz
- BioPol ehf, Einbúastig 2, Skagaströnd 545; Iceland
- Faculty of Natural Resource Sciences; University of Akureyri, Borgir v. Nordurslod; Akureyri IS 600 Iceland
| | - Kensuke Seto
- Department of Environmental Sciences, Faculty of Science; Toho University, 2-2-1, Miyama; Funabashi Chiba 274-8510 Japan
- Sugadaira Montane Research Center; University of Tsukuba, 1278-294, Sugadaira-Kogen; Ueda, Nagano, 386-2204 Japan
| | - Télesphore Sime-Ngando
- Université Clermont Auvergne, UMR CNRS 6023 LMGE, Laboratoire Microorganismes: Génome et Environnement (LMGE); Campus Universitaire des Cézeaux, Impasse Amélie Murat 1, CS 60026, Aubière, 63178 France
| | - Assaf Sukenik
- Kinneret Limnological Laboratory; Israel Oceanographic & Limnological Research, P.O.Box 447; Migdal, 14950 Israel
| | - Dedmer B. Van de Waal
- Department of Aquatic Ecology; Netherlands Institute of Ecology (NIOO-KNAW), Droevendaalsesteeg 10; Wageningen PB 6708 The Netherlands
| | - Silke Van den Wyngaert
- Department of Experimental Limnology; Leibniz-Institute of Freshwater Ecology and Inland Fisheries (IGB), Alte Fischerhuette 2; Stechlin D-16775 Germany
| | - Ellen Van Donk
- Department of Aquatic Ecology; Netherlands Institute of Ecology (NIOO-KNAW), Droevendaalsesteeg 10; Wageningen PB 6708 The Netherlands
- Department of Biology; University of Utrecht, Padualaan 8; Utrecht TB 3508 The Netherlands
| | - Justyna Wolinska
- Department of Ecosystem Research; Leibniz-Institute of Freshwater Ecology and Inland Fisheries (IGB), Müggelseedamm 301; Berlin 12587 Germany
- Institute of Biology, Freie Universität Berlin, Königin-Luise-Straβe 1-3; Berlin, 14195 Germany
| | - Christian Wurzbacher
- Department of Biological and Environmental Sciences; University of Gothenburg, Box 461; Göteborg, 405 30 Sweden
- Gothenburg Global Biodiversity Centre, Box 461; Göteborg, SE-405 30 Sweden
| | - Ramsy Agha
- Department of Ecosystem Research; Leibniz-Institute of Freshwater Ecology and Inland Fisheries (IGB), Müggelseedamm 301; Berlin 12587 Germany
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Marcé R, George G, Buscarinu P, Deidda M, Dunalska J, de Eyto E, Flaim G, Grossart HP, Istvanovics V, Lenhardt M, Moreno-Ostos E, Obrador B, Ostrovsky I, Pierson DC, Potužák J, Poikane S, Rinke K, Rodríguez-Mozaz S, Staehr PA, Šumberová K, Waajen G, Weyhenmeyer GA, Weathers KC, Zion M, Ibelings BW, Jennings E. Automatic High Frequency Monitoring for Improved Lake and Reservoir Management. Environ Sci Technol 2016; 50:10780-10794. [PMID: 27597444 DOI: 10.1021/acs.est.6b01604] [Citation(s) in RCA: 15] [Impact Index Per Article: 1.9] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 05/19/2023]
Abstract
Recent technological developments have increased the number of variables being monitored in lakes and reservoirs using automatic high frequency monitoring (AHFM). However, design of AHFM systems and posterior data handling and interpretation are currently being developed on a site-by-site and issue-by-issue basis with minimal standardization of protocols or knowledge sharing. As a result, many deployments become short-lived or underutilized, and many new scientific developments that are potentially useful for water management and environmental legislation remain underexplored. This Critical Review bridges scientific uses of AHFM with their applications by providing an overview of the current AHFM capabilities, together with examples of successful applications. We review the use of AHFM for maximizing the provision of ecosystem services supplied by lakes and reservoirs (consumptive and non consumptive uses, food production, and recreation), and for reporting lake status in the EU Water Framework Directive. We also highlight critical issues to enhance the application of AHFM, and suggest the establishment of appropriate networks to facilitate knowledge sharing and technological transfer between potential users. Finally, we give advice on how modern sensor technology can successfully be applied on a larger scale to the management of lakes and reservoirs and maximize the ecosystem services they provide.
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Affiliation(s)
- Rafael Marcé
- Catalan Institute for Water Research (ICRA) , Emili Grahit 101, 17003 Girona, Spain
| | - Glen George
- Freshwater Biological Association , 34786 Windermere, U.K
- Department of Geography and Earth Sciences, University of Aberystwyth , Aberystwyth, Ceredigion, SY23 3FL, U.K
| | - Paola Buscarinu
- Ente acque della Sardegna , via Mameli 88, 09123 Cagliari, Italy
| | - Melania Deidda
- Ente acque della Sardegna , via Mameli 88, 09123 Cagliari, Italy
| | - Julita Dunalska
- Department of Water Protection Engineering, University of Warmia and Mazury in Olsztyn , Prawocheńskiego strasse 1, 10-719 Olsztyn, Poland
| | - Elvira de Eyto
- Marine Institute , Furnace, Newport, County Mayo F28 PF65, Ireland
| | - Giovanna Flaim
- Research and Innovation Centre , Foundazione Edmund Mach, 38010 San Michele all' Adige, TN, Italy
| | - Hans-Peter Grossart
- Leibniz-Institute of Freshwater Ecology and Inland Fisheries , Alte Fischerhuette 2, 16775 Stechlin, Germany
- Potsdam University , Institute for Biochemistry and Biology, Maulbeerallee 2, 14469 Potsdam, Germany
| | - Vera Istvanovics
- MTA/BME Water Research Group , Műegyetem rkp. 3, 1111 Budapest, Hungary
| | - Mirjana Lenhardt
- Institute for Biological Research University of Belgrade , Bulevar Despota Stefana 142, 11000 Belgrade, Serbia
| | - Enrique Moreno-Ostos
- Marine Ecology and Limnology Research Group, Department of Ecology, University of Málaga , Campus Universitario de Teatinos S/N, 29071 Málaga, Spain
| | - Biel Obrador
- Department of Ecology, University of Barcelona , Av Diagonal 643, 08028 Barcelona, Spain
| | - Ilia Ostrovsky
- Israel Oceanographic and Limnological Research, Yigal Allon Kinneret Limnological Laboratory , 14850 Migdal, Israel
| | - Donald C Pierson
- Department of Limnology, Evolutionary Biology Centre , Norbyvägen 18 D, 752 36 Uppsala, Sweden
| | - Jan Potužák
- Institute of Botany, The Czech Academy of Sciences , Department of Vegetation Ecology, Lidická 25/27, 602 00 Brno, Czech Republic
| | - Sandra Poikane
- European Commission , Joint Research Centre, Institute for Environment and Sustainability, Via E. Fermi 2749, 21027 Ispra, Varese, Italy
| | - Karsten Rinke
- Helmholtz Centre for Environmental Research (UFZ) , Department of Lake Research, Brückstrasse 3a, D-39114 Magdeburg, Germany
| | - Sara Rodríguez-Mozaz
- Catalan Institute for Water Research (ICRA) , Emili Grahit 101, 17003 Girona, Spain
| | - Peter A Staehr
- Institute of Bioscience, Aarhus University , Frederiksborgvej 399, 4000 Roskilde, Denmark
| | - Kateřina Šumberová
- Institute of Botany, The Czech Academy of Sciences , Department of Vegetation Ecology, Lidická 25/27, 602 00 Brno, Czech Republic
| | - Guido Waajen
- Water Authority Brabantse Delta , P.O. Box 5520, 4801 DZ Breda, The Netherlands
| | - Gesa A Weyhenmeyer
- Department of Ecology and Genetics/Limnology, Uppsala University , Norbyvägen 18D, 75236 Uppsala, Sweden
| | - Kathleen C Weathers
- Cary Institute of Ecosystem Studies , Box AB, Millbrook, New York 12545, United States
| | - Mark Zion
- New York City Department of Environmental Protection , 71 Smith Avenue, Kingston, New York 12401, United States
| | - Bas W Ibelings
- Department F.-A. Forel for Environmental and Aquatic Sciences & Institute for Environmental Sciences, University of Geneva , 66 Boulevard Carl-Vogt, 1211 Geneva, Switzerland
| | - Eleanor Jennings
- Centre for Freshwater and Environmental Studies and Department of Applied Sciences, Dundalk Institute of Technology , Dundalk, County Louth A91 K584, Ireland
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Ibelings BW, Backer LC, Kardinaal WEA, Chorus I. Current approaches to cyanotoxin risk assessment and risk management around the globe. Harmful Algae 2015; 49:63-74. [PMID: 26435706 PMCID: PMC4587991 DOI: 10.1016/j.hal.2014.10.002] [Citation(s) in RCA: 85] [Impact Index Per Article: 9.4] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 05/03/2023]
Abstract
Toxic cyanobacteria became more widely recognized as a potential health hazard in the 1990s, and in 1998 the World Health Organization (WHO) first published a provisional Guideline Value of 1 μg L-1 for microcystin-LR in drinking-water. In this publication we compare risk assessment and risk management of toxic cyanobacteria in 17 countries across all five continents. We focus on the three main (oral) exposure vehicles to cyanotoxins: drinking-water, water related recreational and freshwater seafood. Most countries have implemented the provisional WHO Guideline Value, some as legally binding standard, to ensure the distribution of safe drinking-water with respect to microcystins. Regulation, however, also needs to address the possible presence of a wide range of other cyanotoxins and bioactive compounds, for which no guideline values can be derived due to insufficient toxicological data. The presence of microcystins (commonly expressed as microcystin-LR equivalents) may be used as proxy for overall guidance on risk management, but this simplification may miss certain risks, for instance from dissolved fractions of cylindrospermopsin and cyanobacterial neurotoxins. An alternative approach, often taken for risk assessment and management in recreational waters, is to regulate cyanobacterial presence - as cell numbers or biomass - rather than individual toxins. Here, many countries have implemented a two or three tier alert level system with incremental severity. These systems define the levels where responses are switched from Surveillance to Alert and finally to Action Mode and they specify the short-term actions that follow. Surface bloom formation is commonly judged to be a significant risk because of the elevated concentration of microcystins in a scum. Countries have based their derivations of legally binding standards, guideline values, maximally allowed concentrations (or limits named otherwise) on very similar scientific methodology, but underlying assumptions such as bloom duration, average body size and the amount of water consumed while swimming vary according to local circumstances. Furthermore, for toxins with incomplete toxicological data elements of expert judgment become more relevant and this also leads to a larger degree of variation between countries' thresholds triggering certain actions. Cyanobacterial blooms and their cyanotoxin content are a highly variable phenomenon, largely depending on local conditions, and likely concentrations can be assessed and managed best if the specific conditions of the locality are known and their impact on bloom occurrence are understood. Risk Management Frameworks, such as for example the Water Safety Plan concept of the WHO and the 'bathing water profile' of the European Union are suggested to be effective approaches for preventing human exposure by managing toxic cyanobacteria from catchment to consumer for drinking water and at recreational sites.
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Affiliation(s)
- Bas W. Ibelings
- Institute F.-A. Forel and Institute of Environmental Sciences University of Geneva, 10 Route de Suisse, 1290 Versoix, Switzerland
| | - Lorraine C. Backer
- National Center for Environmental Health, 4770 Buford Highway NE, MS F-57, Chamblee, GA 30341, USA
| | - W. Edwin A. Kardinaal
- KWR, Watercycle Research Institute, Groningenhaven 7, 3433 PE Nieuwegein, The Netherlands
| | - Ingrid Chorus
- German Federal Environment Agency, Corrensplatz 1, 14195 Berlin, Germany
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10
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Van den Wyngaert S, Möst M, Freimann R, Ibelings BW, Spaak P. Hidden diversity in the freshwater planktonic diatom Asterionella formosa. Mol Ecol 2015; 24:2955-72. [PMID: 25919789 DOI: 10.1111/mec.13218] [Citation(s) in RCA: 18] [Impact Index Per Article: 2.0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 02/24/2015] [Revised: 04/23/2015] [Accepted: 04/24/2015] [Indexed: 12/20/2022]
Abstract
Many freshwater and marine algal species are described as having cosmopolitan distributions. Whether these widely distributed morphologically similar algae also share a similar gene pool remains often unclear. In the context of island biogeography theory, stronger spatial isolation deemed typical of freshwater lakes should restrict gene flow and lead to higher genetic differentiation among lakes. Using nine microsatellite loci, we investigate the genetic diversity of a widely distributed freshwater planktonic diatom, Asterionella formosa, across different lakes in Switzerland and the Netherlands. We applied a hierarchical spatial sampling design to determine the geographical scale at which populations are structured. A subset of the isolates was additionally analysed using amplified fragment length polymorphism (AFLP) markers. Our results revealed complex and unexpected population structure in A. formosa with evidence for both restricted and moderate to high gene flow at the same time. Different genetic markers (microsatellites and AFLPs) analysed with a variety of multivariate methods consistently revealed that genetic differentiation within lakes was much stronger than among lakes, indicating the presence of cryptic species within A. formosa. We conclude that the hidden diversity found in this study is expected to have implications for the further use of A. formosa in biogeographical, conservation and ecological studies. Further research using species-level phylogenetic markers is necessary to place the observed differentiation in an evolutionary context of speciation.
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Affiliation(s)
- S Van den Wyngaert
- Aquatic Ecology, Eawag, Ueberlandstrasse 133, PO Box 611, CH-8600, Duebendorf, Switzerland.,Institute of Integrative Biology, ETH Zürich, CH-8092, Zürich, Switzerland.,Experimental Limnology, Leibniz-Institute of Freshwater Ecology and Inland Fisheries (IGB) Berlin, Alte Fischerhütte 2, 16775, Stechlin, Germany
| | - M Möst
- Aquatic Ecology, Eawag, Ueberlandstrasse 133, PO Box 611, CH-8600, Duebendorf, Switzerland.,Institute of Integrative Biology, ETH Zürich, CH-8092, Zürich, Switzerland.,Department of Zoology, University of Cambridge, Downing St., Cambridge, CB2 3EJ, UK
| | - R Freimann
- Institute of Molecular Health Sciences, ETH-Zürich, Otto-Stern-Weg 7, CH-8093, Zürich, Switzerland
| | - B W Ibelings
- Aquatic Ecology, Eawag, Ueberlandstrasse 133, PO Box 611, CH-8600, Duebendorf, Switzerland.,Institute of Integrative Biology, ETH Zürich, CH-8092, Zürich, Switzerland.,Institut F.-A. Forel, Université de Genève, 10 Route de Suisse, CH-12090, Versoix, Switzerland
| | - P Spaak
- Aquatic Ecology, Eawag, Ueberlandstrasse 133, PO Box 611, CH-8600, Duebendorf, Switzerland.,Institute of Integrative Biology, ETH Zürich, CH-8092, Zürich, Switzerland
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Van den Wyngaert S, Vanholsbeeck O, Spaak P, Ibelings BW. Parasite fitness traits under environmental variation: disentangling the roles of a chytrid's immediate host and external environment. Microb Ecol 2014; 68:645-656. [PMID: 24863129 DOI: 10.1007/s00248-014-0434-1] [Citation(s) in RCA: 15] [Impact Index Per Article: 1.5] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 11/29/2013] [Accepted: 05/09/2014] [Indexed: 06/03/2023]
Abstract
Parasite environments are heterogeneous at different levels. The first level of variability is the host itself. The second level represents the external environment for the hosts, to which parasites may be exposed during part of their life cycle. Both levels are expected to affect parasite fitness traits. We disentangle the main and interaction effects of variation in the immediate host environment, here the diatom Asterionella formosa (variables host cell volume and host condition through herbicide pre-exposure) and variation in the external environment (variables host density and acute herbicide exposure) on three fitness traits (infection success, development time and reproductive output) of a chytrid parasite. Herbicide exposure only decreased infection success in a low host density environment. This result reinforces the hypothesis that chytrid zoospores use photosynthesis-dependent chemical cues to locate its host. At high host densities, chemotaxis becomes less relevant due to increasing chance contact rates between host and parasite, thereby following the mass-action principle in epidemiology. Theoretical support for this finding is provided by an agent-based simulation model. The immediate host environment (cell volume) substantially affected parasite reproductive output and also interacted with the external herbicide exposed environment. On the contrary, changes in the immediate host environment through herbicide pre-exposure did not increase infection success, though it had subtle effects on zoospore development time and reproductive output. This study shows that both immediate host and external environment as well as their interaction have significant effects on parasite fitness. Disentangling these effects improves our understanding of the processes underlying parasite spread and disease dynamics.
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Affiliation(s)
- Silke Van den Wyngaert
- Aquatic Ecology, Eawag, Ueberlandstrasse 133, P.O. Box 611, 8600, Duebendorf, Switzerland,
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Matthews B, De Meester L, Jones CG, Ibelings BW, Bouma TJ, Nuutinen V, de Koppel JV, Odling-Smee J. Under niche construction: an operational bridge between ecology, evolution, and ecosystem science. ECOL MONOGR 2014. [DOI: 10.1890/13-0953.1] [Citation(s) in RCA: 124] [Impact Index Per Article: 12.4] [Reference Citation Analysis] [What about the content of this article? (0)] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/18/2022]
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Gsell AS, de Senerpont Domis LN, van Donk E, Ibelings BW. Temperature alters host genotype-specific susceptibility to chytrid infection. PLoS One 2013; 8:e71737. [PMID: 23990982 PMCID: PMC3753301 DOI: 10.1371/journal.pone.0071737] [Citation(s) in RCA: 29] [Impact Index Per Article: 2.6] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Download PDF] [Figures] [Journal Information] [Subscribe] [Scholar Register] [Received: 05/05/2013] [Accepted: 07/09/2013] [Indexed: 11/20/2022] Open
Abstract
The cost of parasitism often depends on environmental conditions and host identity. Therefore, variation in the biotic and abiotic environment can have repercussions on both, species-level host-parasite interaction patterns but also on host genotype-specific susceptibility to disease. We exposed seven genetically different but concurrent strains of the diatom Asterionella formosa to one genotype of its naturally co-occurring chytrid parasite Zygorhizidium planktonicum across five environmentally relevant temperatures. We found that the thermal tolerance range of the tested parasite genotype was narrower than that of its host, providing the host with a “cold” and “hot” thermal refuge of very low or no infection. Susceptibility to disease was host genotype-specific and varied with temperature level so that no genotype was most or least resistant across all temperatures. This suggests a role of thermal variation in the maintenance of diversity in disease related traits in this phytoplankton host. The duration and intensity of chytrid parasite pressure on host populations is likely to be affected by the projected changes in temperature patterns due to climate warming both through altering temperature dependent disease susceptibility of the host and, potentially, through en- or disabling thermal host refugia. This, in turn may affect the selective strength of the parasite on the genetic architecture of the host population.
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Affiliation(s)
- Alena S. Gsell
- Department of Aquatic Ecology, Netherlands Institute of Ecology (NIOO-KNAW), Wageningen, The Netherlands
- * E-mail:
| | | | - Ellen van Donk
- Department of Aquatic Ecology, Netherlands Institute of Ecology (NIOO-KNAW), Wageningen, The Netherlands
- Department of Biology, University of Utrecht, Utrecht, The Netherlands
| | - Bas W. Ibelings
- Department of Aquatic Ecology, Netherlands Institute of Ecology (NIOO-KNAW), Wageningen, The Netherlands
- Microbial Ecology, Institut F.-A. Forel, Université de Genève, Versoix, Switzerland
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14
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Pomati F, Kraft NJB, Posch T, Eugster B, Jokela J, Ibelings BW. Individual cell based traits obtained by scanning flow-cytometry show selection by biotic and abiotic environmental factors during a phytoplankton spring bloom. PLoS One 2013; 8:e71677. [PMID: 23951218 PMCID: PMC3741118 DOI: 10.1371/journal.pone.0071677] [Citation(s) in RCA: 42] [Impact Index Per Article: 3.8] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Download PDF] [Figures] [Journal Information] [Subscribe] [Scholar Register] [Received: 02/07/2013] [Accepted: 07/02/2013] [Indexed: 11/18/2022] Open
Abstract
In ecology and evolution, the primary challenge in understanding the processes that shape biodiversity is to assess the relationship between the phenotypic traits of organisms and the environment. Here we tested for selection on physio-morphological traits measured by scanning flow-cytometry at the individual level in phytoplankton communities under a temporally changing biotic and abiotic environment. Our aim was to study how high-frequency temporal changes in the environment influence biodiversity dynamics in a natural community. We focused on a spring bloom in Lake Zurich (Switzerland), characterized by rapid changes in phytoplankton, water conditions, nutrients and grazing (mainly mediated by herbivore ciliates). We described bloom dynamics in terms of taxonomic and trait-based diversity and found that diversity dynamics of trait-based groups were more pronounced than those of identified phytoplankton taxa. We characterized the linkage between measured phytoplankton traits, abiotic environmental factors and abundance of the main grazers and observed weak but significant correlations between changing abiotic and biotic conditions and measured size-related and fluorescence-related traits. We tested for deviations in observed community-wide distributions of focal traits from random patterns and found evidence for both clustering and even spacing of traits, occurring sporadically over the time series. Patterns were consistent with environmental filtering and phenotypic divergence under herbivore pressure, respectively. Size-related traits showed significant even spacing during the peak of herbivore abundance, suggesting that morphology-related traits were under selection from grazing. Pigment distribution within cells and colonies appeared instead to be associated with acclimation to temperature and water chemistry. We found support for trade-offs among grazing resistance and environmental tolerance traits, as well as for substantial periods of dynamics in which our measured traits were not under selection.
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Affiliation(s)
- Francesco Pomati
- Department of Aquatic Ecology, Swiss Federal Institute of Aquatic Science and Technology (Eawag), Dübendorf, Switzerland.
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15
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Van den Wyngaert S, Gsell AS, Spaak P, Ibelings BW. Herbicides in the environment alter infection dynamics in a microbial host-parasite system. Environ Microbiol 2012; 15:837-47. [DOI: 10.1111/j.1462-2920.2012.02874.x] [Citation(s) in RCA: 7] [Impact Index Per Article: 0.6] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 03/22/2012] [Revised: 07/08/2012] [Accepted: 08/17/2012] [Indexed: 11/30/2022]
Affiliation(s)
| | - Alena S. Gsell
- Department of Aquatic Ecology; Netherlands Institute of Ecology; Droevendaalsesteeg 10; 6708 PB; Wageningen; The Netherlands
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16
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Gsell AS, de Senerpont Domis LN, Przytulska-Bartosiewicz A, Mooij WM, van Donk E, Ibelings BW. GENOTYPE-BY-TEMPERATURE INTERACTIONS MAY HELP TO MAINTAIN CLONAL DIVERSITY IN ASTERIONELLA FORMOSA (BACILLARIOPHYCEAE). J Phycol 2012; 48:1197-1208. [PMID: 27011279 DOI: 10.1111/j.1529-8817.2012.01205.x] [Citation(s) in RCA: 12] [Impact Index Per Article: 1.0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [Track Full Text] [Subscribe] [Scholar Register] [Received: 08/03/2011] [Accepted: 04/19/2012] [Indexed: 06/05/2023]
Abstract
Marine and freshwater phytoplankton populations often show large clonal diversity, which is in disagreement with clonal selection of the most vigorous genotype(s). Temporal fluctuation in selection pressures in variable environments is a leading explanation for maintenance of such genetic diversity. To test the influence of temperature as a selection force in continually (seasonally) changing aquatic systems we carried out reaction norms experiments on co-occurring clonal genotypes of a ubiquitous diatom species, Asterionella formosa Hassall, across an environmentally relevant range of temperatures. We report within population genetic diversity and extensive diversity in genotype-specific reaction norms in growth rates and cell size traits. Our results showed genotype by environment interactions, indicating that no genotype could outgrow all others across all temperature environments. Subsequently, we constructed a model to simulate the relative proportion of each genotype in a hypothetical population based on genotype and temperature-specific population growth rates. This model was run with different seasonal temperature patterns. Our modeling exercise showed a succession of two to several genotypes becoming numerically dominant depending on the underlying temperature pattern. The results suggest that (temperature) context dependent fitness may contribute to the maintenance of genetic diversity in isolated populations of clonally reproducing microorganisms in temporally variable environments.
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Affiliation(s)
- Alena S Gsell
- Department of Aquatic Ecology, Netherlands Institute of Ecology (NIOO-KNAW), 6708 PB, Wageningen, The Netherlands
| | - Lisette N de Senerpont Domis
- Department of Aquatic Ecology, Netherlands Institute of Ecology (NIOO-KNAW), 6708 PB, Wageningen, The Netherlands
| | | | - Wolf M Mooij
- Department of Aquatic Ecology, Netherlands Institute of Ecology (NIOO-KNAW), 6708 PB, Wageningen, The Netherlands
- Department of Aquatic Ecology and Water Quality Management, Wageningen University, 6700 AA, Wageningen, The Netherlands
| | - Ellen van Donk
- Department of Aquatic Ecology, Netherlands Institute of Ecology (NIOO-KNAW), 6708 PB, Wageningen, The Netherlands
- Department of Biology, University of Utrecht, 3584 CH, Utrecht, The Netherlands
| | - Bas W Ibelings
- Department of Aquatic Ecology, Netherlands Institute of Ecology (NIOO-KNAW), 6708 PB, Wageningen, The Netherlands
- Department of Aquatic Ecology, Eawag, 8600, Dübendorf, Switzerland
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17
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Carey CC, Ibelings BW, Hoffmann EP, Hamilton DP, Brookes JD. Eco-physiological adaptations that favour freshwater cyanobacteria in a changing climate. Water Res 2012; 46:1394-407. [PMID: 22217430 DOI: 10.1016/j.watres.2011.12.016] [Citation(s) in RCA: 302] [Impact Index Per Article: 25.2] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 09/21/2011] [Revised: 11/28/2011] [Accepted: 12/06/2011] [Indexed: 05/22/2023]
Abstract
Climate change scenarios predict that rivers, lakes, and reservoirs will experience increased temperatures, more intense and longer periods of thermal stratification, modified hydrology, and altered nutrient loading. These environmental drivers will have substantial effects on freshwater phytoplankton species composition and biomass, potentially favouring cyanobacteria over other phytoplankton. In this Review, we examine how several cyanobacterial eco-physiological traits, specifically, the ability to grow in warmer temperatures; buoyancy; high affinity for, and ability to store, phosphorus; nitrogen-fixation; akinete production; and efficient light harvesting, vary amongst cyanobacteria genera and may enable them to dominate in future climate scenarios. We predict that spatial variation in climate change will interact with physiological variation in cyanobacteria to create differences in the dominant cyanobacterial taxa among regions. Finally, we suggest that physiological traits specific to different cyanobacterial taxa may favour certain taxa over others in different regions, but overall, cyanobacteria as a group are likely to increase in most regions in the future.
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Affiliation(s)
- Cayelan C Carey
- Department of Ecology and Evolutionary Biology, Corson Hall, Cornell University, Ithaca, NY 14853, USA.
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18
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Pomati F, Matthews B, Jokela J, Schildknecht A, Ibelings BW. Effects of re-oligotrophication and climate warming on plankton richness and community stability in a deep mesotrophic lake. OIKOS 2011. [DOI: 10.1111/j.1600-0706.2011.20055.x] [Citation(s) in RCA: 62] [Impact Index Per Article: 4.8] [Reference Citation Analysis] [What about the content of this article? (0)] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/28/2022]
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Pomati F, Jokela J, Simona M, Veronesi M, Ibelings BW. An automated platform for phytoplankton ecology and aquatic ecosystem monitoring. Environ Sci Technol 2011; 45:9658-65. [PMID: 21981777 DOI: 10.1021/es201934n] [Citation(s) in RCA: 26] [Impact Index Per Article: 2.0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 05/12/2023]
Abstract
High quality monitoring data are vital for tracking and understanding the causes of ecosystem change. We present a potentially powerful approach for phytoplankton and aquatic ecosystem monitoring, based on integration of scanning flow-cytometry for the characterization and counting of algal cells with multiparametric vertical water profiling. This approach affords high-frequency data on phytoplankton abundance, functional traits and diversity, coupled with the characterization of environmental conditions for growth over the vertical structure of a deep water body. Data from a pilot study revealed effects of an environmental disturbance event on the phytoplankton community in Lake Lugano (Switzerland), characterized by a reduction in cytometry-based functional diversity and by a period of cyanobacterial dominance. These changes were missed by traditional limnological methods, employed in parallel to high-frequency monitoring. Modeling of phytoplankton functional diversity revealed the importance of integrated spatiotemporal data, including circadian time-lags and variability over the water column, to understand the drivers of diversity and dynamic processes. The approach described represents progress toward an automated and trait-based analysis of phytoplankton natural communities. Streamlining of high-frequency measurements may represent a resource for understanding, modeling and managing aquatic ecosystems under impact of environmental change, yielding insight into processes governing phytoplankton community resistance and resilience.
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Affiliation(s)
- Francesco Pomati
- Department of Aquatic Ecology, Swiss Federal Institute of Aquatic Science and Technology, Eawag, Seestrasse 79, 6047 Kastanienbaum, Switzerland.
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Pires LMD, Sarpe D, Brehm M, Ibelings BW. Potential synergistic effects of microcystins and bacterial lipopolysaccharides on life history traits of Daphnia galeata raised on low and high food levels. Aquat Toxicol 2011; 104:230-242. [PMID: 21635866 DOI: 10.1016/j.aquatox.2011.05.001] [Citation(s) in RCA: 8] [Impact Index Per Article: 0.6] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 01/23/2011] [Revised: 04/21/2011] [Accepted: 05/01/2011] [Indexed: 05/30/2023]
Abstract
Metastudies have found no consistent effects of the cyanobacterial toxin microcystin on Daphnia, and there are discrepancies between field observations and experiments. Confounding factors include absence or presence of alternative high quality food or the presence of bioactive compounds, other than microcystins in cyanobacteria. Of specific interest are lipopolysaccharides (LPS) on the outer cell wall. LPS may have a number of biological effects, including reduced detoxication of microcystins in plants and animals. When grazing seston in the field, filterfeeders take up heterotrophic bacteria attached to cyanobacteria, as well as free-living bacteria. The LPS produced by heterotrophic bacteria have been shown to be much more harmful than cyanobacterial LPS. We performed two experiments in which we tested for potential synergistic effects between bacterial LPS and microcystins. Full-factorial experiments separated the main effects and interactions between (i) food quantity as well as food quality (addition of the green alga Scenedesmus), (ii) presence or absence of strains that vary in amount and composition of microcystins (microcystin free strain NIVA-CYA43, moderate microcystin producing strain NIVA-CYA140 and high microcystin producing strain PCC7820), and (iii) presence or absence of bacterial LPS on different life history traits of Daphnia galeata. We measured juvenile growth rate, age and size at first reproduction, death before first reproduction and standard carbon content of Daphnia. From the experiments we conclude that microcystin-producing Microcystis had deleterious effects on the life history of D. galeata, but especially when the availability of high quality green algal food was limited in comparison to the supply of microcystin producing strain PCC7820. In the experiment in which PCC7820 was used as microcystin-producing strain, addition of LPS lowered SCC of Daphnia, but had no effects on other life history parameters. The interaction between Microcystis strain, Microcystis concentration and LPS was highly significant in case of PCC7820, but not in case of CYA-140, indicating that the effects of LPS and its interactions with microcystin on Daphnia life history were strongly context dependent.
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Affiliation(s)
- L Miguel Dionisio Pires
- Netherlands Institute of Ecology, Department of Aquatic Ecology, 6700 AB Wageningen, The Netherlands
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Aguirre von Wobeser E, Ibelings BW, Bok J, Krasikov V, Huisman J, Matthijs HC. Concerted changes in gene expression and cell physiology of the cyanobacterium Synechocystis sp. strain PCC 6803 during transitions between nitrogen and light-limited growth. Plant Physiol 2011; 155:1445-57. [PMID: 21205618 PMCID: PMC3046598 DOI: 10.1104/pp.110.165837] [Citation(s) in RCA: 28] [Impact Index Per Article: 2.2] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 09/15/2010] [Accepted: 12/08/2010] [Indexed: 05/20/2023]
Abstract
Physiological adaptation and genome-wide expression profiles of the cyanobacterium Synechocystis sp. strain PCC 6803 in response to gradual transitions between nitrogen-limited and light-limited growth conditions were measured in continuous cultures. Transitions induced changes in pigment composition, light absorption coefficient, photosynthetic electron transport, and specific growth rate. Physiological changes were accompanied by reproducible changes in the expression of several hundred open reading frames, genes with functions in photosynthesis and respiration, carbon and nitrogen assimilation, protein synthesis, phosphorus metabolism, and overall regulation of cell function and proliferation. Cluster analysis of the nearly 1,600 regulated open reading frames identified eight clusters, each showing a different temporal response during the transitions. Two large clusters mirrored each other. One cluster included genes involved in photosynthesis, which were up-regulated during light-limited growth but down-regulated during nitrogen-limited growth. Conversely, genes in the other cluster were down-regulated during light-limited growth but up-regulated during nitrogen-limited growth; this cluster included several genes involved in nitrogen uptake and assimilation. These results demonstrate complementary regulation of gene expression for two major metabolic activities of cyanobacteria. Comparison with batch-culture experiments revealed interesting differences in gene expression between batch and continuous culture and illustrates that continuous-culture experiments can pick up subtle changes in cell physiology and gene expression.
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Schriek S, Aguirre-von-Wobeser E, Nodop A, Becker A, Ibelings BW, Bok J, Staiger D, Matthijs HCP, Pistorius EK, Michel KP. Transcript profiling indicates that the absence of PsbO affects the coordination of C and N metabolism in Synechocystis sp. PCC 6803. Physiol Plant 2008; 133:525-543. [PMID: 18419737 DOI: 10.1111/j.1399-3054.2008.01119.x] [Citation(s) in RCA: 5] [Impact Index Per Article: 0.3] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 05/26/2023]
Abstract
Transcript profiling of nitrate-grown Synechocystis sp. PCC 6803 PsbO-free mutant cells in comparison to wild-type (WT) detected substantial deviations. Because we had previously observed phenotypical differences between Synechocystis sp. PCC 6803 WT and its corresponding PsbO-free mutant when cultivated with l-arginine as sole N source and a light intensity of 200 mumol photons m(-2) s(-1), we also performed transcript profiling for both strains grown either with nitrate or with l-arginine as sole N source. We observed a total number of 520 differentially regulated transcripts in Synechocystis WT because of a shift from nitrate- to l-arginine-containing BG11 medium, while we detected only 13 differentially regulated transcripts for the PsbO-free mutant. Thus, the PsbO-free Synechocystis mutant had already undergone a preconditioning process for growth with l-arginine in comparison to WT. While Synechocystis WT suffered from growth with l-arginine at a light intensity of 200 mumol photons m(-2) s(-1), the PsbO-free mutant developed only a minor stress phenotype. In summary, our results suggest that the absence of PsbO in Synechocystis affects the coordination of photosynthesis/respiration and l-arginine metabolism through complex probably redox-mediated regulatory pathways. In addition, we show that a comparison of the transcriptomes of nitrate-grown Synechococcus elongatus PCC 7942 WT cells and its corresponding PsbO-free mutant cells resulted in only a few differentially regulated transcripts between both strains. The absence of the manganese/calcium-stabilizing PsbO protein of PSII with an assigned regulatory function for photosynthetic water oxidation causes bigger changes in the transcriptome of the permissive photoheterotrophically growing Synechocystis sp. PCC 6803 than in the transcriptome of the obligate photoautotrophically growing S. elongatus PCC 7942.
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Affiliation(s)
- Sarah Schriek
- Lehrstuhl für Molekulare Zellphysiologie, Universität Bielefeld, Universitätsstr. 25, D-33615 Bielefeld, Germany
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Kagami M, von Elert E, Ibelings BW, de Bruin A, van Donk E. The parasitic chytrid, Zygorhizidium, facilitates the growth of the cladoceran zooplankter, Daphnia, in cultures of the inedible alga, Asterionella. Proc Biol Sci 2008; 274:1561-6. [PMID: 17439852 PMCID: PMC2176168 DOI: 10.1098/rspb.2007.0425] [Citation(s) in RCA: 107] [Impact Index Per Article: 6.7] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/12/2022] Open
Abstract
In food-web studies, parasites are often ignored owing to their insignificant biomass. We provide evidence that parasites may affect trophic transfer in aquatic food webs. Many phytoplankton species are susceptible to parasitic fungi (chytrids). Chytrid infections of diatoms in lakes may reach epidemic proportions during diatom spring blooms, so that numerous free-swimming fungal zoospores (2-3 microm in diameter) are produced. Analysis shows that these zoospores are rich in polyunsaturated fatty acids and sterols (particularly cholesterol), which indicates that they provide excellent food for zooplankters such as Daphnia. In life-table experiments using the large diatom Asterionella formosa as food, Daphnia growth increased significantly in treatments where a parasite was present. By grazing on the zoospores, Daphnia acquired important supplementary nutrients and were able to grow. When large inedible algae are infected by parasites, nutrients within the algal cells are consumed by these chytrids, some of which, in turn, are grazed by Daphnia. Thus, chytrids transfer energy and nutrients from their hosts to zooplankton. This study suggests that parasitic fungi alter trophic relationships in freshwater ecosystems and may be the important components in shaping the community and the food-web dynamics of lakes.
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Affiliation(s)
- Maiko Kagami
- Department of Foodweb Studies, Netherlands Institute of Ecology (NIOO-KNAW), Centre for Limnology, Rijkstraatweg 6, 3631AC Nieuwersluis, The Netherlands.
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Tuominen I, Pollari M, Aguirre von Wobeser E, Tyystjärvi E, Ibelings BW, Matthijs HCP, Tyystjärvi T. Sigma factor SigC is required for heat acclimation of the cyanobacterium Synechocystis sp. strain PCC 6803. FEBS Lett 2007; 582:346-50. [PMID: 18166156 DOI: 10.1016/j.febslet.2007.12.030] [Citation(s) in RCA: 31] [Impact Index Per Article: 1.8] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 11/27/2007] [Revised: 12/14/2007] [Accepted: 12/18/2007] [Indexed: 11/28/2022]
Abstract
The role of the primary-like sigma factor SigC was studied in Synechocystis. Under high temperature stress (48 degrees C) the DeltasigC inactivation strain showed a lower survival rate than the control strain. The DeltasigC strain grew poorly at 43 degrees C in liquid cultures under normal air. However, change to 3% CO(2) enhanced growth of DeltasigC at 43 degrees C. Differences in expression of many genes related to the carbon concentrating mechanisms between the control and the DeltasigC strain were recorded with a genome-wide DNA microarray. We suggest that low solubility of CO2 at high temperature is one of the factors contributing to the poor thermotolerance of the DeltasigC strain.
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Affiliation(s)
- Ilona Tuominen
- Plant Physiology and Molecular Biology, Department of Biology, University of Turku, Turku, Finland
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Ibelings BW, Chorus I. Accumulation of cyanobacterial toxins in freshwater "seafood" and its consequences for public health: a review. Environ Pollut 2007; 150:177-92. [PMID: 17689845 DOI: 10.1016/j.envpol.2007.04.012] [Citation(s) in RCA: 213] [Impact Index Per Article: 12.5] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 04/13/2007] [Accepted: 04/15/2007] [Indexed: 05/06/2023]
Abstract
This review summarizes and discusses the current understanding of human exposure to cyanobacterial toxins in "seafood" collected from freshwater and coastal areas. The review consists of three parts: (a) the existing literature on concentrations of cyanobacterial toxins in seafood is reviewed, and the likelihood of bioaccumulation discussed; (b) we derive cyanotoxin doses likely to occur through seafood consumption and propose guideline values for seafood and compare these to guidelines for drinking water; and (c) we discuss means to assess, control or mitigate the risks of exposure to cyanotoxins through seafood consumption. This is discussed in the context of two specific procedures, the food specific HACCP-approach and the water-specific Water Safety Plan approach by the WHO. Risks of exposure to cyanotoxins in food are sometimes underestimated. Risk assessments should acknowledge this and investigate the partitioning of exposure between drinking-water and food, which may vary depending on local circumstances.
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Affiliation(s)
- Bas W Ibelings
- Eawag, Swiss Federal Institute of Aquatic Sciences and Technology, Centre of Ecology, Evolution and Biogeochemistry, Seestrasse 79, CH-6047 Kastanienbaum, Switzerland.
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Eisenhut M, Aguirre von Wobeser E, Jonas L, Schubert H, Ibelings BW, Bauwe H, Matthijs HCP, Hagemann M. Long-term response toward inorganic carbon limitation in wild type and glycolate turnover mutants of the cyanobacterium Synechocystis sp. strain PCC 6803. Plant Physiol 2007; 144:1946-59. [PMID: 17600135 PMCID: PMC1949882 DOI: 10.1104/pp.107.103341] [Citation(s) in RCA: 74] [Impact Index Per Article: 4.4] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 06/04/2007] [Accepted: 06/24/2007] [Indexed: 05/16/2023]
Abstract
Concerted changes in the transcriptional pattern and physiological traits that result from long-term (here defined as up to 24 h) limitation of inorganic carbon (C(i)) have been investigated for the cyanobacterium Synechocystis sp. strain PCC 6803. Results from reverse transcription-polymerase chain reaction and genome-wide DNA microarray analyses indicated stable up-regulation of genes for inducible CO(2) and HCO(3)(-) uptake systems and of the rfb cluster that encodes enzymes involved in outer cell wall polysaccharide synthesis. Coordinated up-regulation of photosystem I genes was further found and supported by a higher photosystem I content and activity under low C(i) (LC) conditions. Bacterial-type glycerate pathway genes were induced by LC conditions, in contrast to the genes for the plant-like photorespiratory C2 cycle. Down-regulation was observed for nitrate assimilation genes and surprisingly also for almost all carboxysomal proteins. However, for the latter the observed elongation of the half-life time of the large subunit of Rubisco protein may render compensation. Mutants defective in glycolate turnover (DeltaglcD and DeltagcvT) showed some transcriptional changes under high C(i) conditions that are characteristic for LC conditions in wild-type cells, like a modest down-regulation of carboxysomal genes. Properties under LC conditions were comparable to LC wild type, including the strong response of genes encoding inducible high-affinity C(i) uptake systems. Electron microscopy revealed a conspicuous increase in number of carboxysomes per cell in mutant DeltaglcD already under high C(i) conditions. These data indicate that an increased level of photorespiratory intermediates may affect carboxysomal components but does not intervene with the expression of majority of LC inducible genes.
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Affiliation(s)
- Marion Eisenhut
- Universität Rostock, Institut für Biowissenschaften, Abteilung Pflanzenphysiologie , D-18059 Rostock, Germany; University of Amsterdam, Institute for Biodiversity and Ecosystem Dynamics, NL-1018WS Amsterdam, The Netherlands
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Dionisio Pires LM, Ibelings BW, Brehm M, Van Donk E. Comparing grazing on lake seston by Dreissena and Daphnia: lessons for biomanipulation. Microb Ecol 2005; 50:242-52. [PMID: 16184335 DOI: 10.1007/s00248-004-0147-6] [Citation(s) in RCA: 7] [Impact Index Per Article: 0.4] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 07/13/2004] [Accepted: 11/03/2004] [Indexed: 05/04/2023]
Abstract
Biomanipulation measures in lakes, taken to diminish algal blooms, have mainly been restricted to the reduction of zooplanktivorous fish with the aim to stimulate the grazing pressure by native filter feeders such as Daphnia. However, larger filter feeders like the exotic zebra mussel, Dreissena polymorpha, have been suggested as an optional tool because of their high filtering capacity. We compared grazing by two filter feeders, D. polymorpha and Daphnia galeata, offered seston from Lake IJsselmeer, the Netherlands in two consecutive years: 2002 and 2003. The seston in both years was dominated by the colony-forming cyanobacterium Microcystis aeruginosa. The grazing studies were performed under controlled conditions in the laboratory and samples were analyzed on a flow cytometer, making it possible to quantify grazing on different seston components and size fractions, including cyanobacteria, other phytoplankton (green algae, diatoms, etc.), and detritus. No differences in clearance rates, on a per weight basis, were found between the two grazer species. The clearance rate on cyanobacteria (especially <20 microm) was lower in 2003 than in 2002. In 2003, the microcystin concentration of cyanobacteria was higher than in 2002, suggesting that the observed lower clearance rate in 2003 was due to the enhanced toxin content of the cyanobacteria. Zebra mussels, although indiscriminately filtering all seston groups out of the water, positively selected for phytoplankton in their mantle cavity, irrespective of its toxicity, and rejected detritus. Since no differences in clearance rates were found between the two grazer species, we conclude that for biomanipulation purposes of shallow lakes, native species like the daphnids should be preferred over exotic species like zebra mussels. When the seston is dominated by phytoplankton that cannot be filtered out of the water column by Daphnia, however, the use of zebra mussels may be considered. Care should be taken, however, in the choice of the lakes since the mussels may have severe ecological and economic impacts.
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Affiliation(s)
- L M Dionisio Pires
- NOAA, Great Lakes Environmental Research Laboratory, 2205 Commonwealth Boulevard, Ann Arbor, MI 48105-2945, USA.
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Ibelings BW, Bruning K, de Jonge J, Wolfstein K, Pires LMD, Postma J, Burger T. Distribution of microcystins in a lake foodweb: no evidence for biomagnification. Microb Ecol 2005; 49:487-500. [PMID: 16052377 DOI: 10.1007/s00248-004-0014-x] [Citation(s) in RCA: 37] [Impact Index Per Article: 1.9] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 01/26/2004] [Accepted: 06/24/2004] [Indexed: 05/03/2023]
Abstract
Microcystins, toxins produced by cyanobacteria, may play a role in fish kills, although their specific contribution remains unclear. A better understanding of the eco-toxicological effects of microcystins is hampered by a lack of analyses at different trophic levels in lake foodwebs. We present 3 years of monitoring data, and directly compare the transfer of microcystin in the foodweb starting with the uptake of (toxic) cyanobacteria by two different filter feeders: the cladoceran Daphnia galeata and the zebra mussel Dreissena polymorpha. Furthermore foodwebs are compared in years in which the colonial cyanobacterium Microcystis aeruginosa or the filamentous cyanobacterium Planktothrix agardhii dominated; there are implications in terms of the types and amount of microcystins produced and in the ingestion of cyanobacteria. Microcystin concentrations in the seston commonly reached levels where harmful effects on zooplankton are to be expected. Likewise, concentrations in zooplankton reached levels where intoxication of fish is likely. The food chain starting with Dreissena (consumed by roach and diving ducks) remained relatively free from microcystins. Liver damage, typical for exposure to microcystins, was observed in a large fraction of the populations of different fish species, although no relation with the amount of microcystin could be established. Microcystin levels were especially high in the livers of planktivorous fish, mainly smelt. This puts piscivorous birds at risk. We found no evidence for biomagnification of microcystins. Concentrations in filter feeders were always much below those in the seston, and yet vectorial transport to higher trophic levels took place. Concentrations of microcystin in smelt liver exceeded those in the diet of these fish, but it is incorrect to compare levels in a selected organ to those in a whole organism (zooplankton). The discussion focuses on the implications of detoxication and covalent binding of microcystin for the transfer of the toxin in the foodweb. It seems likely that microcystins are one, but not the sole, factor involved in fish kills during blooms of cyanobacteria.
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Affiliation(s)
- B W Ibelings
- Institute for Inland Water Management and Waste Water Treatment (RIZA), Lelystad, The Netherlands.
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Stomp M, Huisman J, De Jongh F, Veraart AJ, Gerla D, Rijkeboer M, Ibelings BW, Wollenzien UIA, Stal LJ. Adaptive divergence in pigment composition promotes phytoplankton biodiversity. Nature 2004; 432:104-7. [PMID: 15475947 DOI: 10.1038/nature03044] [Citation(s) in RCA: 140] [Impact Index Per Article: 7.0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 07/15/2004] [Accepted: 09/20/2004] [Indexed: 11/08/2022]
Abstract
The dazzling diversity of the phytoplankton has puzzled biologists for decades. The puzzle has been enlarged rather than solved by the progressive discovery of new phototrophic microorganisms in the oceans, including picocyanobacteria, pico-eukaryotes, and bacteriochlorophyll-based and rhodopsin-based phototrophic bacteria. Physiological and genomic studies suggest that natural selection promotes niche differentiation among these phototrophic microorganisms, particularly with respect to their photosynthetic characteristics. We have analysed competition for light between two closely related picocyanobacteria of the Synechococcus group that we isolated from the Baltic Sea. One of these two has a red colour because it contains the pigment phycoerythrin, whereas the other is blue-green because it contains high contents of the pigment phycocyanin. Here we report theory and competition experiments that reveal stable coexistence of the two picocyanobacteria, owing to partitioning of the light spectrum. Further competition experiments with a third marine cyanobacterium, capable of adapting its pigment composition, show that this species persists by investing in the pigment that absorbs the colour not used by its competitors. These results demonstrate the adaptive significance of divergence in pigment composition of phototrophic microorganisms, which allows an efficient utilization of light energy and favours species coexistence.
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Affiliation(s)
- Maayke Stomp
- Aquatic Microbiology, Institute for Biodiversity and Ecosystem Dynamics, University of Amsterdam, Nieuwe Achtergracht 127, 1018 WS Amsterdam, The Netherlands
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Pires LMD, Karlsson KM, Meriluoto JAO, Kardinaal E, Visser PM, Siewertsen K, Donk EV, Ibelings BW. Assimilation and depuration of microcystin-LR by the zebra mussel, Dreissena polymorpha. Aquat Toxicol 2004; 69:385-396. [PMID: 15312721 DOI: 10.1016/j.aquatox.2004.06.004] [Citation(s) in RCA: 40] [Impact Index Per Article: 2.0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 03/17/2004] [Revised: 06/07/2004] [Accepted: 06/20/2004] [Indexed: 05/24/2023]
Abstract
Zebra mussels (Dreissena polymorpha) are an important component of the foodweb of shallow lakes in the Netherlands, amongst others in Lake IJsselmeer, an international important wetland. Large numbers of ducks feed on these mussels in autumn and winter. The mussels are filter feeders and are exposed to high densities of cyanobacteria in summer and autumn. Mussels and cyanobacteria both thrive in Lake IJsselmeer. Apparently the mussels are somehow protected against accumulation of harmful quantities of cyanobacterial toxins. In this study, we investigated the assimilation of the cyanobacterial toxin microcystin-LR (MC-LR) in zebra mussels when fed the toxic cyanobacterium Microcystis aeruginosa as sole food or in a mixture with the eustigmatophyte Nannochloropsis limnetica. After 3 weeks of assimilation we studied the depuration of MC-LR during 3 weeks when the food of the mussels was free of cyanobacteria. These assimilation/depuration experiments were combined with grazing experiments, using the same food treatments. Microcystins were analyzed using liquid chromatography-mass spectrometry (LC-MS); in addition, covalently bound MC were analyzed using the MMPB method. The mussels showed higher clearance rates on Microcystis than on Nannochloropsis. No selective rejection of either phytoplankton species was observed in the excretion products of the mussels. Zebra mussels fed Microcystis as single food, assimilated microcystin-LR relatively fast, and after 1 week the maximum value of free unbound microcystin assimilation (ca. 11 microg g DW(-1)) was attained. For mussels, fed with the mixed food, a maximum of only 3.9 microg g DW(-1) was recorded after 3 weeks. Covalently bound MC never reached high values, with a maximum of approximately 62% of free MC in the 2nd week of the experiment. In the depuration period microcystin decreased rapidly to low values and after 3 weeks only very low amounts of microcystin were detectable. The amount of toxin that accumulated in the mussels would appear to be high enough to cause (liver) damage in diving ducks. However, death by exposure to microcystin seems unlikely. Mussels seem efficient in minimizing the assimilation of microcystin. If it were not for this, mass mortalities of ducks in shallow lakes in the Netherlands would presumably occur on a much more widespread scale than is currently observed.
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Affiliation(s)
- L M Dionisio Pires
- Department of Foodweb Studies, Centre for Limnology, Netherlands Institute of Ecology, Rijksstraatweg 6, 3631 AC Nieuwersluis, The Netherlands.
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Vos RJ, Hakvoort JHM, Jordans RWJ, Ibelings BW. Multiplatform optical monitoring of eutrophication in temporally and spatially variable lakes. Sci Total Environ 2003; 312:221-243. [PMID: 12873412 DOI: 10.1016/s0048-9697(03)00225-0] [Citation(s) in RCA: 10] [Impact Index Per Article: 0.5] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 05/24/2023]
Abstract
Representative spatial patterns of eutrophication variables cannot be produced using traditional in situ sampling techniques. Spatial heterogeneity complicates the study of seasonal and long-term trends and the evaluation of water management policies. Remote sensing, however, with its broad view has the potential to deliver the relevant information. This paper will address the added value of synoptic eutrophication maps to the standard monitoring program of two large, spatially and temporally variable lakes in the Netherlands, Lakes IJssel and Marken. Remote sensing images were obtained from SeaWiFS; and combined with hyperspectral reflectance data from the airborne EPS-a sensor and the shipboard PR-650 spectroradiometer. The PR-650 data were used in selecting the most appropriate algorithms for SeaWiFS and EPS-a. A special algorithm for case II waters with high chlorophyll content was applied to SeaWiFS data to obtain chlorophyll concentrations. Synoptic maps of suspended matter were retrieved using inversion of a model for irradiance reflectance. For the airborne sensor inversion of reflectance was used for both suspended matter and chlorophyll. Satellite and airborne sensors clearly are complementary to each other. Comparison of satellite data with the airborne data and the (scarcely available) in situ data reveal underlying problems with: (i) validation of remote sensing images; and (ii) comparing data at different spatial and temporal scales. In our study, we found a reasonable agreement between different data sources at seasonal time scales, but at shorter time scales the differences can be (much) larger. In situ data suffer from poor reproducibility, related to the natural variability at small spatial scales (patchiness), combined with a significant temporal variability. The standard in situ monitoring program in Lakes IJssel and Marken lacks both the necessary spatial coverage as well as an appropriate sampling frequency. This indicates that for reliable monitoring, a synoptic data set, sampled at a high frequency is required. Remote sensing can partially fulfil this demand but still lacks the demanded frequency, mainly due to regular cloud cover. The answer may be in a multiplatform monitoring approach, as used in our study (combining in situ data with shipboard, airborne and satellite optical data) and in combining monitoring data with models. Satellite remote sensing is most powerful in determining properties that are inherent to the whole lake system, like the overall mean chlorophyll-a concentration. Computational models may meet the demand for a sufficiently high sampling frequency by deterministic interpolation of the data in time.
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Affiliation(s)
- R J Vos
- Institute for Environmental Studies, Free University, De Boelelaan 1115, Amsterdam 1081 HV, The Netherlands.
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Ibelings BW, Kroon BMA, Mur LR. Acclimation of photosystem II in a cyanobacterium and a eukaryotic green alga to high and fluctuating photosynthetic photon flux densities, simulating light regimes induced by mixing in lakes. New Phytol 1994; 128:407-424. [PMID: 33874577 DOI: 10.1111/j.1469-8137.1994.tb02987.x] [Citation(s) in RCA: 32] [Impact Index Per Article: 1.1] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 06/12/2023]
Abstract
Photoacclimation of Scenedesmus protuberans Fritsch and Microcystis aeruginosa Kützing emend. Elenkin to high and fluctuating PPFD was studied in continuous cultures with computer-controlled variable light regimes. The aim of the work was to provide a better understanding of species-specific acclimation to high PPFD (as encountered by cyanobacteria in surface waterblooms), and of suppression of the growth of colony-forming cyanobacteria during periods of prolonged mixing in lakes. The dynamics of a set of variables was followed during the light period, including pigment composition, maximum rate, efficiency and minimum quantum requirement of photosynthesis, PS II cross-sections, and fluorescence variables. Both the green alga and the cyanobacterium displayed strong photo-inhibition of photosynthesis in the sinusoidal light regime, which simulated a natural light regime in the absence of mixing. Pmax , α, QR and the ratio of variable to maximum fluorescence declined, and the number of inactive PS II centres and PS IIβ centres increased towards midday. Introduction of oscillations in the diurnal light regime, simulating different intensities of wind-induced mixing in lakes, mitigated photo-inhibition. Microcystis showed a prompt non-photochemical quenching of fluorescence in all light regimes, even at low to moderate PPFD. The sustained presence of zeaxanthin in Microcystis possibly induced instant, thermal dissipation of excitation energy from the antenna. Microcystis also exhibited a more reluctant acclimation to fluctuating PPFD. Growth rate of Scenedesmus was higher in all light regimes. This implied that if (known) differences in loss processes were ignored, Scenedesmus would outcompete Microcystis in lakes. The results underlined the importance of buoyancy regulation in increasing the daily light dose of cyanobacteria (but at the same time preventing over-excitation), and ultimately in the success in Microcystis in stable lakes.
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Affiliation(s)
- Bas W Ibelings
- Laboratory for Microbiology, University of Amsterdam, Nieuwe Achtergracht 127 1018 WS Amsterdam, The Netherlands
| | - Bernd M A Kroon
- Laboratory for Microbiology, University of Amsterdam, Nieuwe Achtergracht 127 1018 WS Amsterdam, The Netherlands
| | - Luuc R Mur
- Laboratory for Microbiology, University of Amsterdam, Nieuwe Achtergracht 127 1018 WS Amsterdam, The Netherlands
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