Cyanobacteria and Cyanotoxins: Information for Drinking Water Systems
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Guidelines for Design and Sampling for Cyanobacterial Toxin and Taste-And-Odor Studies in Lakes and Reservoirs
Guidelines for Design and Sampling for Cyanobacterial Toxin and Taste-and-Odor Studies in Lakes and Reservoirs Scientific Investigations Report 2008–5038 U.S. Department of the Interior U.S. Geological Survey Photo 1 Photo 3 Photo 2 Front cover. Photograph 1: Beach sign warning of the presence of a cyanobacterial bloom, June 29, 2006 (photograph taken by Jennifer L. Graham, U.S. Geological Survey). Photograph 2: Sampling a near-shore accumulation of Microcystis, August 8, 2006 (photograph taken by Jennifer L. Graham, U.S. Geological Survey). Photograph 3: Mixed bloom of Anabaena, Aphanizomenon, and Microcystis, August 10, 2006 (photograph taken by Jennifer L. Graham, U.S. Geological Survey). Background photograph: Near-shore accumulation of Microcystis, August 8, 2006 (photograph taken by Jennifer L. Graham, U.S. Geological Survey). Guidelines for Design and Sampling for Cyanobacterial Toxin and Taste-and-Odor Studies in Lakes and Reservoirs By Jennifer L. Graham, Keith A. Loftin, Andrew C. Ziegler, and Michael T. Meyer Scientific Investigations Report 2008–5038 U.S. Department of the Interior U.S. Geological Survey U.S. Department of the Interior DIRK KEMPTHORNE, Secretary U.S. Geological Survey Mark D. Myers, Director U.S. Geological Survey, Reston, Virginia: 2008 For product and ordering information: World Wide Web: http://www.usgs.gov/pubprod Telephone: 1-888-ASK-USGS For more information on the USGS—the Federal source for science about the Earth, its natural and living resources, natural hazards, and the environment: World Wide Web: http://www.usgs.gov Telephone: 1-888-ASK-USGS Any use of trade, product, or firm names is for descriptive purposes only and does not imply endorsement by the U.S. -
Anoxygenic Photosynthesis in Photolithotrophic Sulfur Bacteria and Their Role in Detoxication of Hydrogen Sulfide
antioxidants Review Anoxygenic Photosynthesis in Photolithotrophic Sulfur Bacteria and Their Role in Detoxication of Hydrogen Sulfide Ivan Kushkevych 1,* , Veronika Bosáková 1,2 , Monika Vítˇezová 1 and Simon K.-M. R. Rittmann 3,* 1 Department of Experimental Biology, Faculty of Science, Masaryk University, 62500 Brno, Czech Republic; [email protected] (V.B.); [email protected] (M.V.) 2 Department of Biology, Faculty of Medicine, Masaryk University, 62500 Brno, Czech Republic 3 Archaea Physiology & Biotechnology Group, Department of Functional and Evolutionary Ecology, Universität Wien, 1090 Vienna, Austria * Correspondence: [email protected] (I.K.); [email protected] (S.K.-M.R.R.); Tel.: +420-549-495-315 (I.K.); +431-427-776-513 (S.K.-M.R.R.) Abstract: Hydrogen sulfide is a toxic compound that can affect various groups of water microorgan- isms. Photolithotrophic sulfur bacteria including Chromatiaceae and Chlorobiaceae are able to convert inorganic substrate (hydrogen sulfide and carbon dioxide) into organic matter deriving energy from photosynthesis. This process takes place in the absence of molecular oxygen and is referred to as anoxygenic photosynthesis, in which exogenous electron donors are needed. These donors may be reduced sulfur compounds such as hydrogen sulfide. This paper deals with the description of this metabolic process, representatives of the above-mentioned families, and discusses the possibility using anoxygenic phototrophic microorganisms for the detoxification of toxic hydrogen sulfide. Moreover, their general characteristics, morphology, metabolism, and taxonomy are described as Citation: Kushkevych, I.; Bosáková, well as the conditions for isolation and cultivation of these microorganisms will be presented. V.; Vítˇezová,M.; Rittmann, S.K.-M.R. -
Cyanobacterial Peptide Toxins
CYANOBACTERIAL PEPTIDE TOXINS CYANOBACTERIAL PEPTIDE TOXINS 1. Exposure data 1.1 Introduction Cyanobacteria, also known as blue-green algae, are widely distributed in fresh, brackish and marine environments, in soil and on moist surfaces. They are an ancient group of prokaryotic organisms that are found all over the world in environments as diverse as Antarctic soils and volcanic hot springs, often where no other vegetation can exist (Knoll, 2008). Cyanobacteria are considered to be the organisms responsible for the early accumulation of oxygen in the earth’s atmosphere (Knoll, 2008). The name ‘blue- green’ algae derives from the fact that these organisms contain a specific pigment, phycocyanin, which gives many species a slightly blue-green appearance. Cyanobacterial metabolites can be lethally toxic to wildlife, domestic livestock and even humans. Cyanotoxins fall into three broad groups of chemical structure: cyclic peptides, alkaloids and lipopolysaccharides. Table 1.1 gives an overview of the specific toxic substances within these broad groups that are produced by different genera of cyanobacteria together, with their primary target organs in mammals. However, not all cyanobacterial blooms are toxic and neither are all strains within one species. Toxic and non-toxic strains show no predictable difference in appearance and, therefore, physicochemical, biochemical and biological methods are essential for the detection of cyanobacterial toxins. The most frequently reported cyanobacterial toxins are cyclic heptapeptide toxins known as microcystins which can be isolated from several species of the freshwater genera Microcystis , Planktothrix ( Oscillatoria ), Anabaena and Nostoc . More than 70 structural variants of microcystins are known. A structurally very similar class of cyanobacterial toxins is nodularins ( < 10 structural variants), which are cyclic pentapeptide hepatotoxins that are found in the brackish-water cyanobacterium Nodularia . -
Limits of Life on Earth Some Archaea and Bacteria
Limits of life on Earth Thermophiles Temperatures up to ~55C are common, but T > 55C is Some archaea and bacteria (extremophiles) can live in associated usually with geothermal features (hot springs, environments that we would consider inhospitable to volcanic activity etc) life (heat, cold, acidity, high pressure etc) Thermophiles are organisms that can successfully live Distinguish between growth and survival: many organisms can survive intervals of harsh conditions but could not at high temperatures live permanently in such conditions (e.g. seeds, spores) Best studied extremophiles: may be relevant to the Interest: origin of life. Very hot environments tolerable for life do not seem to exist elsewhere in the Solar System • analogs for extraterrestrial environments • `extreme’ conditions may have been more common on the early Earth - origin of life? • some unusual environments (e.g. subterranean) are very widespread Extraterrestrial Life: Spring 2008 Extraterrestrial Life: Spring 2008 Grand Prismatic Spring, Yellowstone National Park Hydrothermal vents: high pressure in the deep ocean allows liquid water Colors on the edge of the at T >> 100C spring are caused by different colonies of thermophilic Vents emit superheated water (300C or cyanobacteria and algae more) that is rich in minerals Hottest water is lifeless, but `cooler’ ~50 species of such thermophiles - mostly archae with some margins support array of thermophiles: cyanobacteria and anaerobic photosynthetic bacteria oxidize sulphur, manganese, grow on methane + carbon monoxide etc… Sulfolobus: optimum T ~ 80C, minimum 60C, maximum 90C, also prefer a moderately acidic pH. Live by oxidizing sulfur Known examples can grow (i.e. multiply) at temperatures which is abundant near hot springs. -
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. -
Protocols for Monitoring Harmful Algal Blooms for Sustainable Aquaculture and Coastal Fisheries in Chile (Supplement Data)
Protocols for monitoring Harmful Algal Blooms for sustainable aquaculture and coastal fisheries in Chile (Supplement data) Provided by Kyoko Yarimizu, et al. Table S1. Phytoplankton Naming Dictionary: This dictionary was constructed from the species observed in Chilean coast water in the past combined with the IOC list. Each name was verified with the list provided by IFOP and online dictionaries, AlgaeBase (https://www.algaebase.org/) and WoRMS (http://www.marinespecies.org/). The list is subjected to be updated. Phylum Class Order Family Genus Species Ochrophyta Bacillariophyceae Achnanthales Achnanthaceae Achnanthes Achnanthes longipes Bacillariophyta Coscinodiscophyceae Coscinodiscales Heliopeltaceae Actinoptychus Actinoptychus spp. Dinoflagellata Dinophyceae Gymnodiniales Gymnodiniaceae Akashiwo Akashiwo sanguinea Dinoflagellata Dinophyceae Gymnodiniales Gymnodiniaceae Amphidinium Amphidinium spp. Ochrophyta Bacillariophyceae Naviculales Amphipleuraceae Amphiprora Amphiprora spp. Bacillariophyta Bacillariophyceae Thalassiophysales Catenulaceae Amphora Amphora spp. Cyanobacteria Cyanophyceae Nostocales Aphanizomenonaceae Anabaenopsis Anabaenopsis milleri Cyanobacteria Cyanophyceae Oscillatoriales Coleofasciculaceae Anagnostidinema Anagnostidinema amphibium Anagnostidinema Cyanobacteria Cyanophyceae Oscillatoriales Coleofasciculaceae Anagnostidinema lemmermannii Cyanobacteria Cyanophyceae Oscillatoriales Microcoleaceae Annamia Annamia toxica Cyanobacteria Cyanophyceae Nostocales Aphanizomenonaceae Aphanizomenon Aphanizomenon flos-aquae -
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 -
Cyanobacterial Toxins: Saxitoxins
WHO/SDE/WSH/xxxxx English only Cyanobacterial toxins: Saxitoxins Background document for development of WHO Guidelines for Drinking-water Quality and Guidelines for Safe Recreational Water Environments Version for Public Review Nov 2019 © World Health Organization 20XX Preface Information on cyanobacterial toxins, including saxitoxins, is comprehensively reviewed in a recent volume to be published by the World Health Organization, “Toxic Cyanobacteria in Water” (TCiW; Chorus & Welker, in press). This covers chemical properties of the toxins and information on the cyanobacteria producing them as well as guidance on assessing the risks of their occurrence, monitoring and management. In contrast, this background document focuses on reviewing the toxicological information available for guideline value derivation and the considerations for deriving the guideline values for saxitoxin in water. Sections 1-3 and 8 are largely summaries of respective chapters in TCiW and references to original studies can be found therein. To be written by WHO Secretariat Acknowledgements To be written by WHO Secretariat 5 Abbreviations used in text ARfD Acute Reference Dose bw body weight C Volume of drinking water assumed to be consumed daily by an adult GTX Gonyautoxin i.p. intraperitoneal i.v. intravenous LOAEL Lowest Observed Adverse Effect Level neoSTX Neosaxitoxin NOAEL No Observed Adverse Effect Level P Proportion of exposure assumed to be due to drinking water PSP Paralytic Shellfish Poisoning PST paralytic shellfish toxin STX saxitoxin STXOL saxitoxinol -
Aquatic Microbial Ecology 69:135
Vol. 69: 135–143, 2013 AQUATIC MICROBIAL ECOLOGY Published online May 28 doi: 10.3354/ame01628 Aquat Microb Ecol A cultivation-independent approach for the genetic and cyanotoxin characterization of colonial cyanobacteria Yannick Lara1, Alexandre Lambion1, Diana Menzel2, Geoffrey A. Codd2, Annick Wilmotte1,* 1Center for Protein Engineering, University of Liège, 4000 Liège, Belgium 2Division of Molecular Microbiology, College of Life Sciences, University of Dundee, Dundee DD1 4HN, UK ABSTRACT: To bypass the constraint of cyanobacterial strain isolation and cultivation, a combina- tion of whole genome amplification (WGA) and enzyme-linked immunoassay (ELISA) for micro- cystin toxins (MCs) was tested on individual colonies of Microcystis and Woronichinia, taken directly from aquatic environments. Genomic DNA of boiled cells was amplified by multiple strand displacement amplification (MDA), followed by several specific PCR reactions to character- ize the genotype of each colony. Sequences of 3 different housekeeping genes (ftsZ, gltX, and recA), of 3 MC biosynthesis genes (mcyA, mcyB, and mcyE), and the Internal Transcribed Spacer (ITS) were analyzed for 11 colonies of Microcystis. MCs were detected and quantified by ELISA in 7 of the 11 Microcystis colonies tested, in agreement with the detection of mcy genes. Sequence types (ST) based on the concatenated sequences of housekeeping genes from cyanobacterial colonies from Belgian water bodies appeared to be endemic when compared to those of strains described in the literature. One colony appeared to belong to a yet undiscovered lineage. A simi- lar protocol was used for 6 colonies of the genus Woronichinia, a taxon that is very difficult to cul- tivate in the laboratory. -
Investigation of a Microcystis Aeruginosa Cyanobacterial Freshwater Harmful Algal Bloom Associated with Acute Microcystin Toxicosis in a Dog
View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by K-State Research Exchange This is the author’s final, peer-reviewed manuscript as accepted for publication. The publisher-formatted version may be available through the publisher’s web site or your institution’s library. Investigation of a Microcystis aeruginosa cyanobacterial freshwater harmful algal bloom associated with acute microcystin toxicosis in a dog Deon van der Merwe, Lionel Sebbag, Jerome C. Nietfeld, Mark T. Aubel, Amanda Foss, Edward Carney How to cite this manuscript If you make reference to this version of the manuscript, use the following information: Van der Merwe, D., Sebbag, L., Nietfeld, J. C., Aubel, M. T., Foss, A., & Carney, E. (2012). Investigation of a Microcystis aeruginosa cyanobacterial freshwater harmful algal bloom associated with acute microcystin toxicosis in a dog. Retrieved from http://krex.ksu.edu Published Version Information Citation: Van der Merwe, D., Sebbag, L., Nietfeld, J. C., Aubel, M. T., Foss, A., & Carney, E. (2012). Investigation of a Microcystis aeruginosa cyanobacterial freshwater harmful algal bloom associated with acute microcystin toxicosis in a dog. Journal of Veterinary Diagnostic Investigation, 24(4), 679-687. Copyright: © 2012 The Author(s) Digital Object Identifier (DOI): doi:10.1177/1040638712445768 Publisher’s Link: http://vdi.sagepub.com/content/24/4/679 This item was retrieved from the K-State Research Exchange (K-REx), the institutional repository of Kansas State University. K-REx is available at http://krex.ksu.edu 1 TITLE PAGE 2 Investigation of a Microcystis aeruginosa cyanobacterial freshwater harmful algal bloom 3 associated with acute microcystin toxicosis in a dog 4 5 Deon van der Merwe1, Lionel Sebbag, Jerome C. -
Harmful Algal Blooms (Habs) Program Guide
HARMFUL ALGAL BLOOMS (HABS) PROGRAM GUIDE www.dec.ny.gov Contents List of Tables ....................................................................................................................ii List of Figures ...................................................................................................................ii Abbreviations and Acronyms ........................................................................................... iii 1. Executive Summary ................................................................................................. 1 2. Introduction .............................................................................................................. 2 2.1. Purpose of this Document ............................................................................... 2 2.2. Scope, Jurisdiction and Audience ................................................................... 2 2.3. Background ..................................................................................................... 2 2.4. Agency Responsibilities .................................................................................. 4 3. DEC Bloom Status Designation in New York ........................................................... 8 3.1. Bloom Status Criteria ...................................................................................... 8 3.2. Threshold Development ................................................................................ 12 3.3. Cyanotoxins and Other Harmful Compounds .............................................. -
PROTISTS Shore and the Waves Are Large, Often the Largest of a Storm Event, and with a Long Period
(seas), and these waves can mobilize boulders. During this phase of the storm the rapid changes in current direction caused by these large, short-period waves generate high accelerative forces, and it is these forces that ultimately can move even large boulders. Traditionally, most rocky-intertidal ecological stud- ies have been conducted on rocky platforms where the substrate is composed of stable basement rock. Projec- tiles tend to be uncommon in these types of habitats, and damage from projectiles is usually light. Perhaps for this reason the role of projectiles in intertidal ecology has received little attention. Boulder-fi eld intertidal zones are as common as, if not more common than, rock plat- forms. In boulder fi elds, projectiles are abundant, and the evidence of damage due to projectiles is obvious. Here projectiles may be one of the most important defi ning physical forces in the habitat. SEE ALSO THE FOLLOWING ARTICLES Geology, Coastal / Habitat Alteration / Hydrodynamic Forces / Wave Exposure FURTHER READING Carstens. T. 1968. Wave forces on boundaries and submerged bodies. Sarsia FIGURE 6 The intertidal zone on the north side of Cape Blanco, 34: 37–60. Oregon. The large, smooth boulders are made of serpentine, while Dayton, P. K. 1971. Competition, disturbance, and community organi- the surrounding rock from which the intertidal platform is formed zation: the provision and subsequent utilization of space in a rocky is sandstone. The smooth boulders are from a source outside the intertidal community. Ecological Monographs 45: 137–159. intertidal zone and were carried into the intertidal zone by waves. Levin, S. A., and R.