Managing Cyanotoxins
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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. -
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 . -
Suspect and Target Screening of Natural Toxins in the Ter River Catchment Area in NE Spain and Prioritisation by Their Toxicity
toxins Article Suspect and Target Screening of Natural Toxins in the Ter River Catchment Area in NE Spain and Prioritisation by Their Toxicity Massimo Picardo 1 , Oscar Núñez 2,3 and Marinella Farré 1,* 1 Department of Environmental Chemistry, IDAEA-CSIC, 08034 Barcelona, Spain; [email protected] 2 Department of Chemical Engineering and Analytical Chemistry, University of Barcelona, 08034 Barcelona, Spain; [email protected] 3 Serra Húnter Professor, Generalitat de Catalunya, 08034 Barcelona, Spain * Correspondence: [email protected] Received: 5 October 2020; Accepted: 26 November 2020; Published: 28 November 2020 Abstract: This study presents the application of a suspect screening approach to screen a wide range of natural toxins, including mycotoxins, bacterial toxins, and plant toxins, in surface waters. The method is based on a generic solid-phase extraction procedure, using three sorbent phases in two cartridges that are connected in series, hence covering a wide range of polarities, followed by liquid chromatography coupled to high-resolution mass spectrometry. The acquisition was performed in the full-scan and data-dependent modes while working under positive and negative ionisation conditions. This method was applied in order to assess the natural toxins in the Ter River water reservoirs, which are used to produce drinking water for Barcelona city (Spain). The study was carried out during a period of seven months, covering the expected prior, during, and post-peak blooming periods of the natural toxins. Fifty-three (53) compounds were tentatively identified, and nine of these were confirmed and quantified. Phytotoxins were identified as the most frequent group of natural toxins in the water, particularly the alkaloids group. -
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. -
Western Lake Erie Harmful Algal Blooms
Harmful Algal Bloom Research Initiative Thomas Bridgeman, PhD University of Toledo Nov 30, 2016 Toledo Water Crisis, August 2014 Algal toxin in treated Toledo water exceeded 1.0 ug/L limit recommended by the WHO ‘Do not drink’ advisory Aug 2-4 500,000 residents temporarily without potable water Lake Erie Water Intake Toledo Blade CBS News Ohio Department of Higher Education Response Major algal groups in Lakes Diatoms Greens Blue-greens (Cyanobacteria) Common Harmful “Algae” (Cyanobacteria) Anabaena Aphanizomenon Microcystis (Dolichospermum) Planktothrix Lyngbya Lyngbya wollei and Microcystis sp. D. Hartsen T. Crail Why are harmful algae harmful? Microcystis toxins Planktothrix toxins Microcystin (FDF) Anatoxin Lyngbyatoxin Aplysiatoxin Anabaena toxins Lyngbya toxins Microcystin Saxitoxin Cylindrospermopsin Lyngbyatoxin Anatoxin (VFDF) Aplysiatoxin Saxitoxin Aphanizomenon toxins Cylindrospermopsin Anatoxin Saxitoxin Freshwater HABs are increasing worldwide Lake Taihu, China Lake Winnipeg Baltic Sea Lake Erie and Grand Lake St. Marys 13-Year Record of HABs August 2002 August 2003 Microcystis HABs in Lake Erie Western Lake Erie Harmful Algal Blooms 40000 35000 Catastrophic 30000 25000 20000 15000 Unacceptable 10000 5000 (ml/m2/y) Biovolume Microcystis Microcystis Biovolume (ml/m2/y) Biovolume Microcystis Acceptable 0 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013 2014 2011 bloom from the International Space Station 2003 Michalak et al. 2013 2014: Winds and water currents concentrated the bloom along the Ohio shore Toledo Water Intake Not a Lake Problem, it’s a LAND problem Ohio Drainage Not just a Northern Ohio Problem Cincinnati Water Intake (H. Raymond, OEPA) The Greening of Lake Erie (Eutrophication) • Between1920 and 1964 Lake Erie algae biomass increased nearly 6 fold. -
Chemical and Biological Study of Aplysiatoxin Derivatives Showing Inhibition of Potassium Cite This: RSC Adv.,2019,9,7594 Channel Kv1.5†
RSC Advances View Article Online PAPER View Journal | View Issue Chemical and biological study of aplysiatoxin derivatives showing inhibition of potassium Cite this: RSC Adv.,2019,9,7594 channel Kv1.5† Yang-Hua Tang,‡ab Jing Wu,‡c Ting-Ting Fan,a Hui-Hui Zhang,a Xiao-Xia Gong,a Zheng-Yu Cao,e Jian Zhang,*c Hou-Wen Lin *d and Bing-Nan Han *a Three new aplysiatoxins, neo-debromoaplysiatoxin D (1), oscillatoxin E (2) and oscillatoxin F (3), accompanied by four known analogues (4–7), were identified from the marine cyanobacterium Lyngbya sp. Structural frames differ amongst these metabolites, and therefore we classified compounds 1 and 4– 6 as aplysiatoxins as they possess 6/12/6 and 6/10/6 tricyclic ring systems featuring a macrolactone ring, and compounds 2, 3 and 7 as oscillatoxins that feature a hexane-tetrahydropyran in a spirobicyclic system. Bioactivity experiments showed that compounds 1 and 4–6 presented significant expression of phosphor-PKCd whereas compounds 2, 5 and 7 showed the most potent blocking activity against Received 5th February 2019 Creative Commons Attribution-NonCommercial 3.0 Unported Licence. potassium channel Kv1.5 with IC values of 0.79 Æ 0.032 mM, 1.28 Æ 0.080 mM and 1.47 Æ 0.138 mM, Accepted 25th February 2019 50 respectively. Molecular docking analysis supplementing the binding interaction of oscillatoxin E (2) and DOI: 10.1039/c9ra00965e oscillatoxin F (3) with Kv1.5 showed oscillatoxin E (2) with a strong binding affinity of À37.645 kcal molÀ1 À rsc.li/rsc-advances and oscillatoxin F (3) with a weaker affinity of À32.217 kcal mol 1, further supporting the experimental data. -
The Spatial and Temporal Distribution and Environmental Drivers Of
THE SPATIAL AND TEMPORAL DISTRIBUTION AND POTENTIAL ENVIRONMENTAL DRIVERS OF SAXITOXIN IN NORTHWEST OHIO Callie A. Nauman A Thesis Submitted to the Graduate College of Bowling Green State University in partial fulfillment of the requirements for the degree of MASTER OF SCIENCE May 2020 Committee: Timothy Davis, Advisor George Bullerjahn Justin Chaffin © 2020 Callie A. Nauman All Rights Reserved iii ABSTRACT Timothy Davis, Advisor Cyanobacterial harmful algal blooms threaten freshwater quality and human health around the world. One specific threat is the ability of some cyanobacteria to produce multiple types of toxins, including a range of neurotoxins called saxitoxins. While it is not completely understood, the general consensus is environmental factors like phosphorus, nitrogen, and light availability, may be driving forces in saxitoxin production. Recent surveys have determined saxitoxin and potential saxitoxin producing cyanobacterial species in both lakes and rivers across the United States and Ohio. Research evaluating benthic cyanobacterial blooms determined benthic cyanobacteria as a source for saxitoxin production in systems, specifically rivers. Currently, little is known about when, where, why, or who is producing saxitoxin in Ohio, and even less is known about the role benthic cyanobacterial blooms play in Ohio waterways. With increased detections of saxitoxin, the saxitoxin biosynthesis gene sxtA, and saxitoxin producing species in both the Western Basin of Lake Erie and the lake’s major tributary the Maumee River, seasonal sampling was conducted to monitor saxitoxin in both systems. The sampling took place from late spring to early autumn of 2018 and 2019. Monitoring including bi-/weekly water column sampling in the Maumee River and Lake Erie and Nutrient Diffusing Substrate (NDS) Experiments, were completed to evaluate saxitoxin, sxtA, potential environmental drivers, and benthic production. -
Author's Personal Copy
Author's personal copy Provided for non-commercial research and educational use only. Not for reproduction, distribution or commercial use. This chapter was originally published in the book Encyclopedia of Toxicology. The copy attached is provided by Elsevier for the author's benefit and for the benefit of the author's institution, for non-commercial research, and educational use. This includes without limitation use in instruction at your institution, distribution to specific colleagues, and providing a copy to your institution's administrator. All other uses, reproduction and distribution, including without limitation commercial reprints, selling or licensing copies or access, or posting on open internet sites, your personal or institution’s website or repository, are prohibited. For exceptions, permission may be sought for such use through Elsevier’s permissions site at: http://www.elsevier.com/locate/permissionusematerial From Hambright, K.D., Zamor, R.M., Easton, J.D., Allison, B., 2014. Algae. In: Wexler, P. (Ed.), Encyclopedia of Toxicology, 3rd edition vol 1. Elsevier Inc., Academic Press, pp. 130–141. ISBN: 9780123864543 Copyright © 2014 Elsevier, Inc. unless otherwise stated. All rights reserved. Academic Press Author's personal copy Algae KD Hambright and RM Zamor, Plankton Ecology and Limnology Laboratory, University of Oklahoma Biological Station, and Program in Ecology and Evolutionary Biology, University of Oklahoma, Norman, OK, USA JD Easton and B Allison, Plankton Ecology and Limnology Laboratory, University of Oklahoma Biological Station, University of Oklahoma, Kingston, OK, USA Ó 2014 Elsevier Inc. All rights reserved. This article is a revision of the previous edition article by Keiko Okamoto and Lora E. Fleming, volume 1, pp 68–76, Ó 2005, Elsevier Inc. -
Running Head: CYANOBACTERIA, Β-METHYLAMINO-L-ALANINE
Running head: CYANOBACTERIA, b-METHYLAMINO-L-ALANINE, AND NEURODEGENERATION Cyanobacteria, β-Methylamino-L-Alanine, and Neurodegeneration Jonathan Hunyadi Lourdes University CYANOBACTERIA, b-METHYLAMINO-L-ALANINE, AND NEURODEGENERATION 2 ABSTRACT Research has found a potential link between the non-proteinogenic amino acid b-methylamino-L-alanine (BMAA) and neurodegenerative diseases. First identified on the island of Guam with a rare form of amyotrophic lateral sclerosis (ALS) commonly called “Guam disease”, the source of BMAA was identified to be cyanobacteria. Due primarily to eutrophication, cyanobacteria can form large “algal blooms” within water bodies. A major concern during cyanobacterial blooms is the production of high concentrations of cyanotoxins such as BMAA. Cyanotoxin biosynthesis is dependent on the presence of specific genes as well as environmental regulating factors. Numerous techniques are capable of analyzing cyanobacteria and cyanotoxins which include: microscopy, pigment spectroscopy, polymerase chain reaction, microarrays, enzyme-linked immunosorbent assays, and liquid chromatography. Liquid chromatography is the primary technique used to analyze BMAA, however, there has been controversy regarding its detection within nervous tissue samples. While BMAAs role in neurodegeneration is unclear, dietary intake has been demonstrated to produce both b-amyloid plaques and tau tangles within Vervet monkeys, hallmarks of both Alzheimer’s disease and Guam disease. Two of the dominant hypothesized mechanisms of BMAA neurotoxicity are glutamate excitotoxicity, by which BMAA functions as a glutamate agonist causing endoplasmic reticulum stress and initiates a cascade leading to tau hyperphosphorylation, and protein incorporation, by which BMAA enters neurons and becomes mis-incorporated within proteins, leading to misfolding and aggregation. As a result of this research, alanine supplements have entered clinical trials for both Alzheimer’s disease and ALS to compete with BMAA in protein incorporation. -
Harmful Algal Blooms (Habs) and Desalination: a Guide to Impacts, Monitoring, and Management
Manuals and Guides 78 Harmful Algal Blooms (HABs) and Desalination: A Guide to Impacts, Monitoring, and Management Edited by: Donald M. Anderson, Siobhan F.E. Boerlage, Mike B. Dixon UNESCO Manuals and Guides 78 Intergovernmental Oceanographic Commission Harmful Algal Blooms (HABs) and Desalination: A Guide to Impacts, Monitoring and Management Edited by: Donald M. Anderson* Biology Department, Woods Hole Oceanographic Institution Woods Hole, MA 02543 USA Siobhan F. E. Boerlage Boerlage Consulting Gold Coast, Queensland, Australia Mike B. Dixon MDD Consulting, Kensington Calgary, Alberta, Canada *Corresponding Author’s email: [email protected] UNESCO 2017 Bloom prevention and control 7 BLOOM PREVENTION AND CONTROL Clarissa R. Anderson1, Kevin G. Sellner2, and Donald M. Anderson3 1University of California, Santa Cruz, Santa Cruz, CA USA 2Chesapeake Research Consortium, Edgewater MD USA 3Woods Hole Oceanographic Institution, Woods Hole MA USA 7.1 Introduction ........................................................................................................................................... 205 7.2 Bloom prevention .................................................................................................................................. 207 7.2.1 Nutrient load reduction .................................................................................................................. 207 7.2.2 Nutrient load ................................................................................................................................. -
Cyanobacteria and Cyanotoxin Analysis and Testing Services [As of 3/15/2016]
Cyanobacteria/Cyanotoxin Testing Services List Developed by the NEIWPCC HAB Workgroup (Northeast state health and environmental agency staff). The New England Interstate Water Pollution Control Commission is a non-profit organization established through an act of Congress in 1947. NEIWPCC strives to: coordinate activities and forums that encourage cooperation among the states; educate the public about key environmental issues; support research projects, train environmental professionals, and provide overall leadership in the management and protection of water quality. Cyanobacteria and Cyanotoxin Analysis and Testing Services [As of 3/15/2016] Disclaimer: Individuals and/or companies listed below have been identified as performing services related to cyanobacteria and cyanotoxin analysis. This should not be considered an endorsement by NEIWPCC or any state agency of their qualifications. Public Water Systems considering contracting with any individual or company should verify that they have the adequate training and are competent to perform the work for which they are being considered. Prices should be viewed as guidelines of what to expect for each lab, rather than final quotes – many offer discounts, e.g., for bulk samples. Academy of Natural Sciences – Phycology Section Patrick Center for Environmental Research 1900 Benjamin Franklin Parkway Philadelphia, PA 19103 Tel: (215) 299-1080 Fax: (215) 299-1079 Email General: [email protected] Email Don Charles: [email protected] Email Frank Acker (primary soft-algae taxonomist): [email protected] Services: Identification of algae and algal measurements/biovolume, cell counts, chlorophyll Pricing: (Can give estimate based on sample, and separate the phytoplankton and periphyton in terms of how they are processed) Semiquantitative count (relative abundance, five-point scale, rare to abundant) – $150-200 Algal identification (cell count, biovolume) – $440-550 Chlorophyll (fluorometer) – Call for cost Diatom count – $300 Aquatic Services, Wayne Carmichael, Ph.D.