DOCSLIB.ORG

Quantitative Observations of Cyanobacteria and Dinoflagellata in Reservoirs of Sri Lanka

Total Page：16

File Type：pdf, Size：1020Kb

Download full-text PDF Read full-text
Quantitative Observations of Cyanobacteria and Dinoflagellata in Reservoirs of Sri Lanka Ceylon Journal of Science 46(4) 2017: 55-68 DOI: http://doi.org/10.4038/cjs.v46i4.7468 RESEARCH ARTICLE Quantitative observations of Cyanobacteria and Dinoflagellata in reservoirs of Sri Lanka P.A.A.P.K. Senanayake1, 2 and S.K. Yatigammana3* 1Medical Research Institute, Colombo 08, Sri Lanka 2Postgraduate Institute of Science, University of Peradeniya, Peradeniya, Sri Lanka 3Department of Zoology, Faculty of Science, University of Peradeniya, Peradeniya, Sri Lanka Received: 14/06/2017; Accepted: 20/10/2017 Abstract:. Cyanobacterial and dinoflagellate blooms especially during the dry periods (Piyasiri, 1995; have a range of social, environmental and economic Pathmalal and Piyasiri 1995). When considering impacts due to their potential of toxin production the water resources of Sri Lanka, the country under extreme environmental conditions. Therefore, possesses over 10,000 operational reservoirs the present study aimed to understand the species where majority are important as irrigational and abundance, distribution and the relationship between species distribution and measured environmental recreational water bodies while a few are variables within the 45 reservoirs studied, covering important in hydroelectricity generation three major climatic regions of Sri Lanka (Wet, (Maddumabandara et al., 1995). Intermediate and Dry). Plankton samples were obtained using a 34µm plankton net. Both field and Cyanobacterial blooms have an array of laboratory analyses were conducted to obtain social, environmental and economic impacts limnological data of each reservoir. Multivariate (Chorus and Bartram, 1999). The production of statistical techniques were used to understand the toxic substances by a relatively small number of species distribution along measured environmental species that commonly occur in freshwater lakes gradients. Thirteen species of Cyanobacteria were and rivers can have a direct effect on human identified and seven of them were toxigenic. The Dry health (Hunter, 1992; Sethunge and Manage, Zone showed the highest diversity of Cyanobacteria including toxigenic species and the Wet Zone showed 2010). These “cyanotoxins” are usually either the lowest. While Cylindrospermopsis raciborskii was hepatotoxic or neurotoxic in pathology and have the dominant species recorded in 22% of the sampled been related to several cases of human sickness reservoirs, Pseudoanabaena limnetica was the least and death, as well as various occurrences of dominant. Only one species of Dinoflagellate, animal mortality (Falconer, 2005; Kuiper- Peridinium aciculiferum was identified from all the Goodman et al., 1999; Manage et al, 2009; climatic regions. Multivariate statistical analysis Manage et al., 2010). Cyanobacteria are revealed that temperature is the most important frequently present together with other environmental variable that determines the species photosynthetic organisms in mesotrophic waters, variation and abundance among the sites. the common genera being Microcystis, Keywords: Cyanobacteria, Cylindrospermopsis, Synechococcus, Anacystis, Gloeocapsa, dinoflagellata, environmental variables, toxigenic Agmenellum (syn. Merismopedia) as unicellular phytoplankton. and colonial types and Oscillatoria, Lyngbya, Spirulina, Ananbaena, Aphanizomenon, Nostoc, INTRODUCTION Cylindrospermopsis, Planktothrix, Calothrix, Rivularia and Gleoetrichia as filamentous types Cyanobacteria are the most ancient (Kulasooriya, 2011). photosynthetic phytoplankton of the planet Earth that shows an ubiquitous distribution The members of the Dinoflagellata live in (Kulasooriya, 2011). The input of nutrients from both fresh and sea water and many have the natural and anthropogenic sources creates ability to produce toxins. Majority of toxin eutrophic conditions, which lead to the producing species live in marine systems while development of algal blooms especially few freshwater dinoflagellates produce toxins Cyanobacteria in water. Such algal blooms have during unfavorable environmental conditions. been recorded in Sri Lankan freshwaters, Among the toxic dinoflagellates, Peridinium *Corresponding Author’s Email: [email protected] http://orcid.org/0000-0001-6002-8855 56 Ceylon Journal of Science 46(4) 2017: 55-68 polonicum, P. willei, P. volzii and P. aciculiferum evaluate the seasonal variations of the have been identified as common freshwater limnological variables (e.g. Perera et al., 2012; species (Niese et al., 2007). Among them, Yatigammna et al., 2013; Yatigammana and Peridinium aciculiferum, known to produce a Cumming, 2016) no studies have been conducted biological toxin, has already been recorded from to understand the relationship of environmental Sri Lankan drinking water reservoirs conditions and phytoplankton especially, toxin (Yatigammana and Perera, 2017; Yatigammana producing species. Therefore, the factors et al., 2011; Sethunge & Pathmalal,2010; Idroos affecting the distribution of phytoplankton et al., 2017). including toxic algae is not completely understood in Sri Lankan waters. Since However freshwater harmful algal blooms environmental variables which indicate the are generally caused by pelagic Cyanobacteria climatic changes do not occur independently of (Carmichael 2001; 2008). It has been suggested each other, but simultaneously (O‟neil et al., that increasing temperature could benefit 2012), it is important to consider how the Cyanobacteria, both directly and indirectly via interactions of those variables could affect spatial increased thermal stratification (Paerl and distribution of organisms to understand what Huisman, 2008). Nevertheless, it is widely environmental variables are the most important accepted that harmful algal blooms are in explaining the variation of species. As multifaceted events, typically caused by the Cyanobacteria and Dianoflagellata are also combination of multiple environmental factors capable of predicting environmental changes, occurring simultaneously (Heisler et al., 2008). understanding of their distribution in reservoirs The governance of Cyanobacteria in aquatic located in different climatic regions should help ecosystems is frequently linked with CO2 understand what environmental variables are availability (Shapiro, 1990; Caraco and Miller, important in describing species variation under 1998), high temperatures (Bouvy et al., 2000; different environmental conditions. Huszar et al., 2000; Figueredo and Giani, 2009; Soares et al., 2009a), high pH (Reynolds and Hence, this study is focused on i) studying Walsby, 1975; Briand et al., 2002) and high and comparing water quality parameters of concentrations of nutrients (especially selected reservoirs in three major climatic phosphorus) (Watson et al., 1997). Furthermore, regions of Sri Lanka (Wet, Intermediate and Dry some Cyanobacteria show decreased cell division Zone); ii) assessing the relationship between rates in response to lower pH conditions (Shapiro species diversity, abundance and measured and Wright, 1990; Whitton and Potts, 2000; environmental variables within the study Czerny et al., 2009). Though many eukaryotic reservoirs; iii) identifying potential causes for phytoplankton cannot tolerate changes in environmental conditions which promote the salinity, a number of Cyanobacterial species have growth of toxgenic species; iv) proposing the euryhaline ability. Therefore changes in suitable remedial measures. salinity may influence community composition as well as potential toxin concentrations and MATERIALS AND METHODS distribution (Laamanen et al., 2002; Orr et al., 2004; Tonk et al., 2007). Site selection During recent times, there has been much Study sites were selected considering the age, concern in the processes influencing the growth climatic region, catchment characteristics, of phytoplankton communities mainly in relation morphometry, biological composition and known to physico-chemical factors (Akbay et al., 1999; algal outbreaks within the recent five years. Peerapornpisal et al., 1999; Elliott et al., 2002). Considering the reservoir density forty five (45) However, most of the studies on Sri Lankan reservoirs from the three major climatic regions reservoirs have been focused on the composition of Sri Lanka (Wet, Intermediate and Dry Zone) and diversity of planktonic algae (e.g. were selected including five (05) from Wet Zone, Abeywickrama, 1979; Rott 1983; Silva, 2013). fourteen (14) from Intermediate Zone and twenty In addition to a few studies carried out to six (26) from the Dry Zone (Figure 1). P.A.A.P.K. Senanayake and S.K. Yatigammana 57 Figure 1: Locations of the 45 study reservoirs in Sri Lanka. The country is divided into three main climatic regions: the Dry Zone, the Intermediate Zone and Wet Zone. Sample collection Steps were taken to complete the biological analysis as early as possible with a maximum Collection of water samples for the biological delay of 48 hrs. Samples were observed using a and limnological analysis was done from July, research microscope (Olympus CX 31) equipped 2015 to March, 2016. For the chemical analysis with phase contrast optics. The species were samples were collected from 0.3m below the air- identified to the lowest possible taxonomical water interface close to the middle and at least level using standard identification guides (e.g. from four other sites identified from each Bellinger and Sigee (2010), Abeywickrama reservoir. (1979)). Relative abundance of each taxon was Collection of Biological data calculated using the following equation to understand the abundance of Cyanobacteria
Load more

Recommended publications
  • Microcystis Sp. Co-Producing Microcystin and Saxitoxin from Songkhla Lake Basin, Thailand
    toxins Article Microcystis Sp. Co-Producing Microcystin and Saxitoxin from Songkhla Lake Basin, Thailand Ampapan Naknaen 1, Waraporn Ratsameepakai 2, Oramas Suttinun 1,3, Yaowapa Sukpondma 4, Eakalak Khan 5 and Rattanaruji Pomwised 6,* 1 Environmental Assessment and Technology for Hazardous Waste Management Research Center, Faculty of Environmental Management, Prince of Songkla University, Hat Yai 90110, Thailand; [email protected] (A.N.); [email protected] (O.S.) 2 Office of Scientific Instrument and Testing, Prince of Songkla University, Hat Yai 90110, Thailand; [email protected] 3 Center of Excellence on Hazardous Substance Management (HSM), Bangkok 10330, Thailand 4 Division of Physical Science, Faculty of Science, Prince of Songkla University, Hat Yai 90110, Thailand; [email protected] 5 Department of Civil and Environmental Engineering and Construction, University of Nevada, Las Vegas, NV 89154-4015, USA; [email protected] 6 Division of Biological Science, Faculty of Science, Prince of Songkla University, Hat Yai 90110, Thailand * Correspondence: [email protected]; Tel.: +66-74-288-325 Abstract: The Songkhla Lake Basin (SLB) located in Southern Thailand, has been increasingly polluted by urban and industrial wastewater, while the lake water has been intensively used. Here, we aimed to investigate cyanobacteria and cyanotoxins in the SLB. Ten cyanobacteria isolates were identified as Microcystis genus based on16S rDNA analysis. All isolates harbored microcystin genes, while five of them carried saxitoxin genes. On day 15 of culturing, the specific growth rate and Chl-a content were 0.2–0.3 per day and 4 µg/mL. The total extracellular polymeric substances (EPS) content was Citation: Naknaen, A.; 0.37–0.49 µg/mL.
    [Show full text]
  • State of the Science for Cyanobacterial Blooms (Microcystis Species) in Florida a Summary Document from the 2019 Harmful Algal Bloom State of the Science Symposium
    State of the Science for Cyanobacterial Blooms (Microcystis species) in Florida A summary document from the 2019 Harmful Algal Bloom State of the Science Symposium Image: Cyanobacterial bloom in Lake Okeechobee Credit: L. Krimsky, Florida Sea Grant Contents: Introduction In recent years, intense blooms of Karenia brevis red tide and Introduction.....................................................2 Microcystis aeruginosa cyanobacteria, known commonly as Current Understanding.....................................3 blue-green algae, have plagued Florida waterways, impacting the state’s economy, environment and public health. Though Bloom Initiation, Development notable in their duration and intensity, these harmful algal and Termination...............................................3 blooms, or HABs, are not uncommon. Florida experiences a variety of HABs in its marine and fresh waters. Public Health....................................................4 Bloom Prediction and Modeling .......................5 In 2019, Governor Ron DeSantis’ Executive Order 19-12 established the Blue-Green Algae Task Force and revived the Bloom Detection and Monitoring......................5 state’s Harmful Algal Bloom Task Force to provide technical expertise and recommendations to reduce the adverse Bloom Mitigation and Control...........................6 impacts of future blooms. Next Steps........................................................6 This fact sheet represents the latest science-based Conclusion.......................................................6
    [Show full text]
  • Planktothrix Agardhii É a Mais Comum
    Accessing Planktothrix species diversity and associated toxins using quantitative real-time PCR in natural waters Catarina Isabel Prata Pereira Leitão Churro Doutoramento em Biologia Departamento Biologia 2015 Orientador Vitor Manuel de Oliveira e Vasconcelos, Professor Catedrático Faculdade de Ciências iv FCUP Accessing Planktothrix species diversity and associated toxins using quantitative real-time PCR in natural waters The research presented in this thesis was supported by the Portuguese Foundation for Science and Technology (FCT, I.P.) national funds through the project PPCDT/AMB/67075/2006 and through the individual Ph.D. research grant SFRH/BD65706/2009 to Catarina Churro co-funded by the European Social Fund (Fundo Social Europeu, FSE), through Programa Operacional Potencial Humano – Quadro de Referência Estratégico Nacional (POPH – QREN) and Foundation for Science and Technology (FCT). The research was performed in the host institutions: National Institute of Health Dr. Ricardo Jorge (INSA, I.P.), Lisboa; Interdisciplinary Centre of Marine and Environmental Research (CIIMAR), Porto and Centre for Microbial Resources (CREM - FCT/UNL), Caparica that provided the laboratories, materials, regents, equipment’s and logistics to perform the experiments. v FCUP Accessing Planktothrix species diversity and associated toxins using quantitative real-time PCR in natural waters vi FCUP Accessing Planktothrix species diversity and associated toxins using quantitative real-time PCR in natural waters ACKNOWLEDGMENTS I would like to express my gratitude to my supervisor Professor Vitor Vasconcelos for accepting to embark in this research and supervising this project and without whom this work would not be possible. I am also greatly thankful to my co-supervisor Elisabete Valério for the encouragement in pursuing a graduate program and for accompanying me all the way through it.
    [Show full text]
  • The Fate of Microcystins in the Environment and Challenges for Monitoring
    Toxins 2014, 6, 3354-3387; doi:10.3390/toxins6123354 OPEN ACCESS toxins ISSN 2072-6651 www.mdpi.com/journal/toxins Review The Fate of Microcystins in the Environment and Challenges for Monitoring Justine R. Schmidt 1,*, Steven W. Wilhelm 2 and Gregory L. Boyer 1 1 Department of Chemistry, College of Environmental Science and Forestry, State University of New York, Syracuse, NY 13210, USA; E-Mail: [email protected] 2 Department of Microbiology, University of Tennessee, Knoxville, TN 37996-0845, USA; E-Mail: [email protected] * Author to whom correspondence should be addressed; E-Mail: [email protected]; Tel.: +1-315-470-6844; Fax: +1-315-470-6856. External Editor: Lesley V. D'Anglada Received: 1 November 2014; in revised form: 29 November 2014 / Accepted: 5 December 2014 / Published: 12 December 2014 Abstract: Microcystins are secondary metabolites produced by cyanobacteria that act as hepatotoxins in higher organisms. These toxins can be altered through abiotic processes, such as photodegradation and adsorption, as well as through biological processes via metabolism and bacterial degradation. Some species of bacteria can degrade microcystins, and many other organisms metabolize microcystins into a series of conjugated products. There are toxicokinetic models used to examine microcystin uptake and elimination, which can be difficult to compare due to differences in compartmentalization and speciation. Metabolites of microcystins are formed as a detoxification mechanism, and little is known about how quickly these metabolites are formed. In summary, microcystins can undergo abiotic and biotic processes that alter the toxicity and structure of the microcystin molecule. The environmental impact and toxicity of these alterations and the metabolism of microcystins remains uncertain, making it difficult to establish guidelines for human health.
    [Show full text]
  • Harmful Cyanobacteria Blooms and Their Toxins In
    Harmful cyanobacteria blooms and their toxins in Clear Lake and the Sacramento-San Joaquin Delta (California) 10-058-150 Surface Water Ambient Monitoring Program (SWAMP) Prepared for: Central Valley Regional Water Quality Control Board 11020 Sun Center Drive, Suite 200 Rancho Cordova, CA 95670 Prepared by: Cécile Mioni (Project Director) & Raphael Kudela (Project co-Director) University of California, Santa Cruz - Institute of Marine Sciences Dolores Baxa (Project co-Director) University of California, Davis – School of Veterinary Medicine Contract manager: Meghan Sullivan Central Valley Regional Water Quality Control Board _________________ With technical contributions by: Kendra Hayashi (Project manager), UCSC Thomas Smythe (Field Officer) and Chris White, Lake County Water Resources Scott Waller (Field Officer) and Brianne Sakata, EMP/DWR Tomo Kurobe (Molecular Biologist), UCD David Crane (Toxicology), DFG-WPCL Kim Ward, SWRCB/DWQ Lenny Grimaldo (Assistance for Statistic Analyses), Bureau of Reclamation Peter Raimondi (Assistance for Statistic Analyses), UCSC Karen Tait, Lake County Health Office Abstract Harmful cyanobacteria and their toxins are growing contaminants of concern. Noxious toxins produced by HC, collectively referred as cyanotoxins, reduce the water quality and may impact the supply of clean water for drinking as well as the water quality which directly impacts the livelihood of other species including several endangered species. USEPA recently (May 29, 2008) made the decision to add microcystin toxins as an additional cause of impairment for the Klamath River, CA. However, harmful cyanobacteria are some of the less studied causes of impairment in California water bodies and their distribution, abundance and dynamics, as well as the conditions promoting their proliferation and toxin production are not well characterized.
    [Show full text]
  • National Wetland DIRECTORY of Sri Lanka
    National Wetland DIRECTORY of Sri Lanka Central Environmental Authority National Wetland Directory of Sri Lanka This publication has been jointly prepared by the Central Environmental Authority (CEA), The World Conservation Union (IUCN) in Sri Lanka and the International Water Management Institute (IWMI). The preparation and printing of this document was carried out with the financial assistance of the Royal Netherlands Embassy in Sri Lanka. i The designation of geographical entities in this book, and the presentation of the material do not imply the expression of any opinion whatsoever on the part of the CEA, IUCN or IWMI concerning the legal status of any country, territory, or area, or of its authorities, or concerning the delimitation of its frontiers or boundaries. The views expressed in this publication do not necessarily reflect those of the CEA, IUCN or IWMI. This publication has been jointly prepared by the Central Environmental Authority (CEA), The World Conservation Union (IUCN) Sri Lanka and the International Water Management Institute (IWMI). The preparation and publication of this directory was undertaken with financial assistance from the Royal Netherlands Government. Published by: The Central Environmental Authority (CEA), The World Conservation Union (IUCN) and the International Water Management Institute (IWMI), Colombo, Sri Lanka. Copyright: © 2006, The Central Environmental Authority (CEA), International Union for Conservation of Nature and Natural Resources and the International Water Management Institute. Reproduction of this publication for educational or other non-commercial purposes is authorised without prior written permission from the copyright holder provided the source is fully acknowledged. Reproduction of this publication for resale or other commercial purposes is prohibited without prior written permission of the copyright holder.
    [Show full text]
  • Practical Success of Biomanipulation Using Filter-Feeding Fish to Control
    Research Article TheScientificWorld (2001) 1, 337–356 ISSN 1532-2246; DOI 10.1100/tsw.2001.67 Practical Success of Biomanipulation using Filter-feeding Fish to Control Cyanobacteria Blooms A Synthesis of Decades of Research and Application in a Subtropical Hypereutrophic Lake Ping Xie* and Jiankang Liu Donghu Experimental Station of Lake Ecosystems, The State Key Laboratory for Freshwater Ecology and Biotechnology of China, Institute of Hydrobiology, Chinese Academy of Sciences, Wuhan 430072, P.R. China Email: [email protected]; [email protected] Received June 11, 2001; Revised June 25, 2001; Accepted June 25, 2001; Published August 8, 2001 Lake Donghu is a 32-km2 shallow, subtropical lake near the Yangtze River (P.R. China) that has experienced dramatic changes in the past five decades. These changes include: (1) a trophic state change from mesotrophy to hypertrophy; (2) dense blooms of cyanobacteria during every summer from the 1970s to 1984; (3) a cessation of blooms starting in 1985, with no recurrence; and (4) an increase, coincident with bloom declines, in the production of silver and bighead carp (filter-feeders) by more than tenfold. There are several possible explanations for the disappearance of blooms, including changes in nutrient concentrations, increased zooplankton grazing, and increased grazing on algae by fish. The long- term data suggest that changes in nutrients or in zooplankton were not important, but that the remarkably increased fish densities might have played the key role. To test this hypothesis, in situ enclosure experiments were conducted in three years. The main conclusions are as follows: (1) an increased stocking of the lake with carp played a decisive role in the elimination of cyanobacteria blooms; (2) both silver and bighead carp can eliminate cyanobacteria blooms directly by grazing; (3) zooplankton cannot suppress the blooms; and (4) the lake still is vulnerable to the outbreak of blooms, should fish grazing decline.
    [Show full text]
  • Microcystis Aeruginosa: Source of Toxic Microcystins in Drinking Water
    African Journal of Biotechnology Vol. 3 (3), pp. 159-168, March 2004 Available online at http://www.academicjournals.org/AJB ISSN 1684–5315 © 2004 Academic Journals Review Microcystis aeruginosa: source of toxic microcystins in drinking water Oberholster PJ1, Botha A-M2* and Grobbelaar JU1 1Department of Plant Sciences, Faculty of Natural and Agricultural Sciences, University of the Free State, PO Box 339, Bloemfontein, ZA9300 2Department of Genetics, Forestry and Agriculture Biotechnology Institute, University of Pretoria, Hillcrest, Pretoria, ZA0002, South Africa Accepted 21 December 2003 Cyanobacteria are one of the earth’s most ancient life forms. Evidence of their existence on earth, derived from fossil records, encompasses a period of some 3.5 billion years in the late Precambrian era. Cyanobacteria are the dominant phytoplanton group in eutrophic freshwater bodies worldwide. They have caused animal poisoning in many parts of the world and may present risks to human health through drinking and recreational activity. Cyanobacteria produce two main groups of toxin namely neurotoxins and peptide hepatotoxins. They were first characterized from the unicellular species, Microcystis aeruginosa, which is the most common toxic cyanobacterium in eutrophic freshwater. The association of environmental parameters with cyanobacterial blooms and the toxicity of microcystin are discussed. Also, the synthesis of the microcystins, as well as the mode of action, control and analysis methods for quantitation of the toxin is reviewed. Key words: Cyanobacteria, microcystins, mcyB gene, PCR-RFLP. INTRODUCTION Cyanobacteria are the dominant phytoplankton group in other accessory pigments are grouped together in rods eutrophic freshwater bodies (Davidson, 1959; Negri et al., and discs that are called phycobilisomes that are 1995).
    [Show full text]
  • Accumulation and Depuration of Microcystin Produced by the Cyanobacterium Microcystis in a Freshwater Snail
    Limnology (2003) 4:131–138 © The Japanese Society of Limnology 2003 DOI 10.1007/s10201-003-0106-1 RESEARCH PAPER Kazuhiko Ozawa · Atsushi Yokoyama · Kanako Ishikawa Michio Kumagai · Mariyo F. Watanabe · Ho-Dong Park Accumulation and depuration of microcystin produced by the cyanobacterium Microcystis in a freshwater snail Received: October 25, 2002 / Accepted: August 19, 2003 Abstract Seasonal changes in microcystin concentrations in Introduction a resident snail (Sinotaia histrica) and an edible clam (Cor- bicula sandai) in Lake Biwa were surveyed. To clarify both the accumulation and depuration of microcystins, experi- The occurrence of toxic cyanobacterial blooms in eutrophic mental studies with microcystin were also carried out on the lakes, reservoirs, and recreational waters has become a snail. In the field investigation, microcystin was detected worldwide problem. In Japanese lakes, the toxic cyano- from the hepatopancreas and intestine of S. histrica (up to bacteria are mainly composed of Microcystis (Park et al. 3.2µggϪ1 dry weight and 19.5µggϪ1 dry weight, respec- 1998), which commonly produces microcystin. Microcystin tively); however, no microcystin was detected in the hepato- is known to be a potent hepatotoxin (Carmichael 1994) and pancreas of C. sandai. In the laboratory experiment, the tumor promoter (Nishiwaki-Matsushima et al. 1991, 1992). microcystin-LR concentration in the hepatopancreas of S. Microcystin is composed of seven amino acids, including a histrica reached a value of 436µggϪ1 dry weight on day 10 of unique amino acid called Adda [3-amino-9-methoxy-2, 6, 8- 15 days of uptake, and a high value persisted despite a trimethyl-10-phenyldeca-4, 6-dienoic acid] (Botes et al.
    [Show full text]
  • Microcystis Aeruginosa in a Central Chilean (36° Lat
    Almanza et al. Revista Chilena de Historia Natural (2016) 89:8 Revista Chilena de DOI 10.1186/s40693-016-0057-7 Historia Natural RESEARCH Open Access Occurrence of toxic blooms of Microcystis aeruginosa in a central Chilean (36° Lat. S) urban lake Viviana Almanza1,2*, Oscar Parra1, Carlos E. De M. Bicudo4,CarolinaBaeza1, Johana Beltran1, Ricardo Figueroa1,3 and Roberto Urrutia1,3 Abstract Background: During the last decades the frequency and global distribution of toxic cyanobacteria blooms has increased globally, which has been attributed to the eutrophication and climate change. In Chile there have been reports on blooms in aquatic ecosystem in localities with high density population and on the presence of five congeners of microcystins but only two documented toxics blooms with hundreds fish kills. We investigated the presence of toxic cyanobacteria blooms in the Lo Galindo urban lake, Concepción city, and the environmental factors that influence the abundance of cyanobacteria and microcystins concentration. Lo Galindo Lake, is used for various recreational and eventually as a drinking water source. Results: Toxic blooms of Microcystis aeruginosa are developed in Lo Galindo lake, those that occur throughout the year in a wide range of environmental conditions, forming scums blooms during summer and dispersive blooms in all seasons. There are different microcystin congeners, the most frequent congener was MC-RR (21 %) and the highest concentration corresponded to 115.4 µg L-1 MC-LR. Conclusions: The dominance and development of the M. aeruginosa blooms in the lake is determined by various environmental factors such as temperature, nutrients, diversity of taxa and wind speed that affect the formation of disperse-type blooms and/or scums; the latter are developed only in summer, coinciding with the highest temperature and concentrations of total microcystins.
    [Show full text]
  • Field Guide to Algae and Other “Scums” in Ponds, Lakes, Streams and Rivers
    The Boone and Kenton County Conservation Districts, Burlington, KY The Campbell County Conservation District, Alexandria, KY Field guide to algae and other “scums” in ponds, lakes, streams and rivers Miriam Steinitz Kannan and Nicole Lenca Northern Kentucky University Field Guide to algae and other “scums” TABLE OF CONTENTS Page Introduction Purpose of the guide—How to use the guide 3 Floating Macroscopic Plants Duckweeds (Lemna, Spirodella) 4 Watermeal (Wolffia) 4 Waterferns (Azolla) 4 Floating Cyanobacteria (Blue-Green Algae) Microcystis 5 Aphanizomenon 6 Anabaena 7 Floating or attached Cyanobacteria (Blue-Green Algae) Oscillatoria, Lyngbya, Phormidium, Plankthotrix 8 Attached Cyanobacteria (Blue-Green Algae) Nostoc 9 Euglena and other flagellated algae Euglena, Phacus, Dinobryon, Prymnesium and Dinoflagellates 10 Diatom Blooms 11 Filamentous Green Algae Spirogyra, Mougeotia and Zygnema 12 Cladophora and Hydrodictyon 13 Bacterial Scums Iron Bacteria -Sphaerotilus 14 Protozoan Scums 15 Zooplankton scums 16 Algae control methods 17 Recommended Web sites 18 Acknowledgements 19 2 Introduction Purpose of this Guide This guide is intended for individuals who work with farm ponds, for watershed groups, homeowners and anyone interested in quickly identifying an algal bloom or scum that appears in a freshwater system. Such blooms usually appear during the summer and fall in temperate regions. Most blooms are the result of nutrient enrichment of the waterway. Of significant concern are blue-green algal blooms (cyanobacteria). Some of these produce liver and/or brain toxins that can be lethal to most fish and livestock. Some of the toxins can also be carcinogenic. The macroscopic appearance of many different genera of algae can be similar and therefore field identification must be verified by using a compound microscope.
    [Show full text]
  • Adsorption Strategy for Removal of Harmful Cyanobacterial Species Microcystis Aeruginosa Using Chitosan Fiber
    sustainability Article Adsorption Strategy for Removal of Harmful Cyanobacterial Species Microcystis aeruginosa Using Chitosan Fiber 1, 1,2, 1 3, 1, Yun Hwan Park y, Sok Kim y, Ho Seon Kim , Chulhwan Park * and Yoon-E Choi * 1 Division of Environmental Science & Ecological Engineering, Korea University, Seoul 02841, Korea; [email protected] (Y.H.P.); [email protected] (S.K.); [email protected] (H.S.K.) 2 BK21 Plus Eco-Leader Education Center, Korea University, Seoul 02841, Korea 3 Department of Chemical Engineering, Kwangwoon University, Seoul 01897, Korea * Correspondence: [email protected] (C.P.); [email protected] (Y.-EC.) The authors equally contributed to the present study. y Received: 17 April 2020; Accepted: 1 June 2020; Published: 4 June 2020 Abstract: Microcystis aeruginosa is one of the predominant species responsible for cyanobacterial-harmful algal blooms (Cyano-HABs) in water bodies. Cyano-HABs pose a growing number of serious threats to the environment and public health. Therefore, the demand for developing safe and eco-friendly solutions to control Cyano-HABs is increasing. In the present study, the adsorptive strategy using chitosan was applied to remove M. aeruginosa cells from aqueous phases. Using a simple immobilization process, chitosan could be fabricated as a fiber sorbent (chitosan fiber, CF). By application of CF, almost 89% of cyanobacterial cells were eliminated, as compared to those in the control group. Field emission scanning electron microscopy proved that the M. aeruginosa cells were mainly attached to the surface of the sorbent, which was correlated well with the measurement of the surface area of the fiber.
    [Show full text]