Recommended Human Health Recreational Ambient Water Quality Criteria Or Swimming Advisories for Microcystins and Cylindrospermopsin

Total Page:16

File Type:pdf, Size:1020Kb

Recommended Human Health Recreational Ambient Water Quality Criteria Or Swimming Advisories for Microcystins and Cylindrospermopsin United States Office of Water EPA 822-R-19-001 Environmental Mail Code 4304T May 2019 Protection Agency Recommended Human Health Recreational Ambient Water Quality Criteria or Swimming Advisories for Microcystins and Cylindrospermopsin Recommended Human Health Recreational Ambient Water Quality Criteria or Swimming Advisories for Microcystins and Cylindrospermopsin Prepared by: U.S. Environmental Protection Agency Office of Water (4304T) Health and Ecological Criteria Division Washington, DC EPA Document Number: 822-R-19-001 Date: May 2019 NOTICES This document has been drafted and approved for publication by the Health and Ecological Criteria Division, Office of Science and Technology, United States Environmental Protection Agency, and is approved for publication. Mention of trade names or commercial products does not constitute endorsement or recommendation for use. Recommended Human Health Recreational Ambient Water Quality Criteria or 3 Swimming Advisories for Microcystins and Cylindrospermopsin FOREWORD Section 304(a) of the Clean Water Act (CWA) requires the Administrator of the U.S. Environmental Protection Agency (EPA) to publish water quality criteria that accurately reflect the latest scientific knowledge on the kind and extent of all identifiable effects on health and welfare that might be expected from the presence of pollutants in any body of water, including ground water. The EPA is publishing these recommended values under CWA 304(a) for states to consider as the basis for swimming advisories for notification purposes in recreational waters to protect the public. The EPA envisions that if states decide to use the values as swimming advisory values they might do so in a manner similar to their current recreational water advisory programs. Alternatively, states may consider using these same values when adopting new or revised water quality standards (WQS). If adopted by states as WQS and approved by the EPA under CWA 303(c), the WQS could be used for all CWA purposes. States may also wish to consider using these values as both swimming advisory values and WQS. This document has undergone an EPA intra-agency peer-review process. The Health and Ecological Criteria Division, Office of Science and Technology, Office of Water, U.S. Environmental Protection Agency has completed the final review and the document is approved for publication. The values were derived using the existing peer-reviewed and published science on the adverse human health effects of the toxins including previous EPA analysis, such as the EPA’s Health Effects Support Document for the Cyanobacterial Toxin Microcystins and Health Effects Support Document for the Cyanobacterial Toxin Cylindrospermopsin (HESDs), and the EPA’s Drinking Water Health Advisory for the Cyanobacterial Microcystin Toxins and Drinking Water Health Advisory for the Cyanobacterial Toxin Cylindrospermopsin (Drinking Water Health Advisories) (U.S. EPA 2015a, 2015b, 2015c, 2015d). The EPA used established criteria methodologies (U.S. EPA 2000) and recreation-specific exposure parameters from the EPA’s Exposure Factors Handbook (EFH) (U.S. EPA 2011) to derive these values. Detailed information that can be found in the EPA’s HESDs and Drinking Water Health Advisories is summarized in this document. The term “water quality criteria” is used in two sections of the CWA section 304(a)(1) and section 303(c)(2). The term has a different legal meaning in each section. In section 304, the term represents a non-regulatory, scientific assessment of effects on human health or aquatic life. The criteria recommendations presented in this document are such a scientific assessment. If the state or authorized tribe adopts water quality criteria associated with specific designated uses as WQS under section 303, and approved by the EPA, they become applicable CWA WQS in ambient waters within that state or tribe. Water quality criteria adopted in state or tribal WQS could have the same numerical values as criteria developed by the EPA under section 304. Alternatively, states and authorized tribes may derive numeric criteria based on other scientifically defensible methods, but the criteria must be protective of designated uses. States and tribes can adopt criteria into their standards. When approved by the EPA, the criteria become Clean Water Act-applicable WQS. Guidelines to assist in modifying the criteria recommendations presented in this document are contained in the Water Quality Standards Handbook (U.S. EPA 2012). This document provides recommendations only. It does not establish or affect legal rights or obligations. It does not establish a binding norm and cannot be finally determinative of the issues addressed. Agency decisions in any particular situation will be made by applying the CWA and EPA regulations on the basis of specific facts presented and scientific information then available. Recommended Human Health Recreational Ambient Water Quality Criteria or 4 Swimming Advisories for Microcystins and Cylindrospermopsin ACKNOWLEDGMENTS The development of this document was made possible through an effort led by John Ravenscroft, EPA Project Manager, Health and Ecological Criteria Division, Office of Science and Technology, Office of Water. The following Office of Science and Technology staff provided valuable contributions to the development and review of this document: Tracy Bone, Dr. Lesley D’Anglada, Dr. Joyce Donohue, Lars Wilcut, Oakridge Institute for Science and Education (ORISE) fellow Meghann Niesen, and summer intern Ana-Maria Murphy-Teixidor. The EPA gratefully acknowledges the valuable contributions of the EPA internal technical reviewers who reviewed this document. Staff from the following EPA program and regional offices completed a formal review of these Human Health Recreational Ambient Water Quality Criteria (AWQC) or Swimming Advisories for Microcystins and Cylindrospermopsin. U.S. EPA Office of Children’s Health Protection U.S. EPA Office of General Counsel U.S. EPA Office of Policy U.S. EPA Office of Research and Development U.S. EPA Office of Water Office of Ground Water and Drinking Water Office of Science and Technology Office of Wastewater Management Office of Wetlands, Oceans, and Watersheds U.S. EPA Regional Offices Region 1 Region 4 Region 5 Region 7 Region 8 Technical support was provided by ICF and its subcontractor Bigelow Laboratory for Ocean Sciences under EPA Contract No. EP-C-16-011. The EPA acknowledges important input received from the states, tribes, local governmental agencies, individual citizens, and stakeholder groups, such as the Association of Clean Water Administrators, and other nongovernmental organizations, who submitted comments on the draft. Recommended Human Health Recreational Ambient Water Quality Criteria or 5 Swimming Advisories for Microcystins and Cylindrospermopsin TABLE OF CONTENTS NOTICES ........................................................................................................................................ 3 FOREWORD .................................................................................................................................. 4 ACKNOWLEDGMENTS .............................................................................................................. 5 TABLE OF CONTENTS ................................................................................................................ 6 LIST OF TABLES .......................................................................................................................... 9 LIST OF FIGURES ...................................................................................................................... 11 ACRONYMS AND ABBREVIATIONS ..................................................................................... 12 1.0 EXECUTIVE SUMMARY ................................................................................................... 15 2.0 INTRODUCTION AND BACKGROUND .......................................................................... 18 International and State Guidelines ............................................................................................ 18 3.0 NATURE OF THE STRESSORS ......................................................................................... 26 3.1 Cyanobacteria and Cyanobacterial Blooms ....................................................................... 26 3.1.1 Environmental Factors Influencing Occurrence of Cyanobacteria and Cyanotoxins ............................................................................................................ 28 3.2 Cyanotoxins ........................................................................................................................ 35 3.2.1 Chemical and Physical Properties ............................................................................ 35 3.2.2 Sources and Occurrence in Surface Waters ............................................................. 38 3.2.3 Estuarine and Marine Waters ................................................................................... 44 3.2.4 Other Sources of Microcystins and Cylindrospermopsin ........................................ 45 3.3 Environmental Fate ............................................................................................................ 45 3.3.1 Mobility.................................................................................................................... 45 3.3.2 Persistence...............................................................................................................
Recommended publications
  • 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 .
    [Show full text]
  • Clinical Biochemistry of Hepatotoxicity
    linica f C l To o x l ic a o n r l o u g Singh, J Clinic Toxicol 2011, S:4 o y J Journal of Clinical Toxicology DOI: 10.4172/2161-0495.S4-001 ISSN: 2161-0495 ReviewResearch Article Article OpenOpen Access Access Clinical Biochemistry of Hepatotoxicity Anita Singh1, Tej K Bhat2 and Om P Sharma2* 1CSK Himachal Pradesh, Krishi Vishva Vidyalaya, Palampur (HP) 176 062, India 2Biochemistry Laboratory, Indian Veterinary Research Institute, Regional Station, Palampur (HP) 176 061, India Abstract Liver plays a central role in the metabolism and excretion of xenobiotics which makes it highly susceptible to their adverse and toxic effects. Liver injury caused by various toxic chemicals or their reactive metabolites [hepatotoxicants) is known as hepatotoxicity. The present review describes the biotransformation of hepatotoxicants and various models used to study hepatotoxicity. It provides an overview of pathological and biochemical mechanism involved during hepatotoxicity together with alteration of clinical biochemistry during liver injury. The review has been supported by a list of important hepatotoxicants as well as common hepatoprotective herbs. Keywords: Hepatotoxicity; Hepatotoxicant; In Vivo models; In Vitro production of bile thus leading to the body’s inability to flush out the models; Pathology; Alanine aminotransferase; Alkaline phosphatase; chemicals through waste. Smooth endoplasmic reticulum of the liver is Bilirubin; Hepatoprotective the principal ‘metabolic clearing house’ for both endogenous chemicals like cholesterol, steroid hormones, fatty acids and proteins, and Introduction exogenous substances like drugs and alcohol. The central role played by liver in the clearance and transformation of chemicals exposes it to Hepatotoxicity refers to liver dysfunction or liver damage that is toxic injury [4].
    [Show full text]
  • Cyanobacterial Bioactive Molecules — an Overview of Their Toxic Properties
    701 REVIEW / SYNTHE` SE Cyanobacterial bioactive molecules — an overview of their toxic properties Pranita Jaiswal, Pawan Kumar Singh, and Radha Prasanna Abstract: Allelopathic interactions involving cyanobacteria are being increasingly explored for the pharmaceutical and en- vironmental significance of the bioactive molecules. Among the toxic compounds produced by cyanobacteria, the biosyn- thetic pathways, regulatory mechanisms, and genes involved are well understood, in relation to biotoxins, whereas the cytotoxins are less investigated. A range of laboratory methods have been developed to detect and identify biotoxins in water as well as the causal organisms; these methods vary greatly in their degree of sophistication and the information they provide. Direct molecular probes are also available to detect and (or) differentiate toxic and nontoxic species from en- vironmental samples. This review collates the information available on the diverse types of toxic bioactive molecules pro- duced by cyanobacteria and provides pointers for effective exploitation of these biologically and industrially significant prokaryotes. Key words: cyanobacteria, bioactive molecules, cyanotoxins, NRP (non-ribosomal peptide), biocontrol agent. Re´sume´ : Les effets alle´lopathiques des cyoanobacte´ries sont de plus en explore´s pour identifier les mole´cules bioactives importantes d’un point de vue pharmaceutique ou environnemental. Parmi les compose´s toxiques produits par les cyano- bacte´ries, les biotoxines sont bien connues quant aux voies, aux me´canismes re´gulateurs et aux ge`nes implique´s dans leur biosynthe`se, alors que les cytotoxines sont moins e´tudie´es. Une varie´te´ de me´thodes de laboratoire ont e´te´ de´veloppe´es afin de de´tecter et d’identifier les biotoxines de l’eau et les agents qui en sont responsables; elles diffe`rent grandement quant a` leur degre´ de sophistication et a` l’information qu’elles ge´ne`rent.
    [Show full text]
  • 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.
    [Show full text]
  • 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
    [Show full text]
  • 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.
    [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]
  • Cylindrospermopsis Raciborskii. Retrieved From
    Cyanobacterium Cylindro I. Current Status and Distribution Cylindrospermopsis raciborskii (previously Anabaenopsis raciborskii) a. Range Global/Continental Wisconsin Native Range Great Lakes strain may have originated in South America1 Figure 1: U.S. Distribution Map2 Figure 2: Midwest Distribution Map2 Abundance/Range Widespread: Tropical and subtropical regions1 Not applicable Locally Abundant: Some temperate areas of northern Lake Michigan basin6, Lake hemisphere1; low levels of toxins Erie1, and a few southern reported in Indiana3 Wisconsin lakes; however there are no detectable toxins4 Sparse: Undocumented Undocumented Range Expansion Date Introduced: First described in Indonesian island of 1980’s or earlier4 Java, 19125 Rate of Spread: Rapid under optimal conditions; Rapid in temperate regions; 357,592 cells/mL in Lake Lemon, U.S. strain may have Indiana3 originated in South America1 Density Risk of Monoculture: High High Facilitated By: Warm temperature, eutrophic Warm temperature, eutrophic conditions conditions b. Habitat Lakes, reservoirs, streams, rivers, ponds, shallow systems Tolerance Chart of tolerances: Increasingly dark color indicates increasingly optimal range1,6,,,,,,7 8 9 10 11 12 Page 1 of 7 Wisconsin Department of Natural Resources – Aquatic Invasive Species Literature Review Preferences Low flow; low water level; low nitrogen to phosphorous ratio; high water temperature; stable thermal stratification; increased retention time; high pH; high sulfate concentration; anoxia in at least some strata; high turbidity; high incident irradiation; low macrophyte biomass1; high total phosphorus and chl-a3; requires high levels of reactive phosphorous13,14 c. Regulation Noxious/Regulated: Not regulated Minnesota Regulations: Not regulated Michigan Regulations: Not regulated Washington Regulations: Secondary Species of Concern II. Establishment Potential and Life History Traits a.
    [Show full text]
  • The Report: Killer Heat in the United States
    Killer Heat in the United States Climate Choices and the Future of Dangerously Hot Days Killer Heat in the United States Climate Choices and the Future of Dangerously Hot Days Kristina Dahl Erika Spanger-Siegfried Rachel Licker Astrid Caldas John Abatzoglou Nicholas Mailloux Rachel Cleetus Shana Udvardy Juan Declet-Barreto Pamela Worth July 2019 © 2019 Union of Concerned Scientists The Union of Concerned Scientists puts rigorous, independent All Rights Reserved science to work to solve our planet’s most pressing problems. Joining with people across the country, we combine technical analysis and effective advocacy to create innovative, practical Authors solutions for a healthy, safe, and sustainable future. Kristina Dahl is a senior climate scientist in the Climate and Energy Program at the Union of Concerned Scientists. More information about UCS is available on the UCS website: www.ucsusa.org Erika Spanger-Siegfried is the lead climate analyst in the program. This report is available online (in PDF format) at www.ucsusa.org /killer-heat. Rachel Licker is a senior climate scientist in the program. Cover photo: AP Photo/Ross D. Franklin Astrid Caldas is a senior climate scientist in the program. In Phoenix on July 5, 2018, temperatures surpassed 112°F. Days with extreme heat have become more frequent in the United States John Abatzoglou is an associate professor in the Department and are on the rise. of Geography at the University of Idaho. Printed on recycled paper. Nicholas Mailloux is a former climate research and engagement specialist in the Climate and Energy Program at UCS. Rachel Cleetus is the lead economist and policy director in the program.
    [Show full text]
  • Phycogeography of Freshwater Phytoplankton: Traditional Knowledge and New Molecular Tools
    Hydrobiologia (2016) 764:3–27 DOI 10.1007/s10750-015-2259-4 PHYTOPLANKTON & SPATIAL GRADIENTS Review Paper Phycogeography of freshwater phytoplankton: traditional knowledge and new molecular tools Judit Padisa´k • Ga´bor Vasas • Ga´bor Borics Received: 29 November 2014 / Revised: 6 March 2015 / Accepted: 14 March 2015 / Published online: 31 March 2015 Ó Springer International Publishing Switzerland 2015 Abstract ‘‘Everything is everywhere, but environ- relevant for biogeography of freshwater phytoplank- ments selects.’’ Is this true? The cosmopolitan nature ton. The following topics are considered: dispersal of algae, including phytoplankton, has been highlight- agents and distances; survival strategies of species; ed in many textbooks and burnt into the minds of geographic distribution of different types; patterns of biologists during their studies. However, the accumu- invasions; tools of molecular genetics; and metabo- lating knowledge on the occurrence of individual lomics to explore dispersal patterns, island biogeog- phytoplankton species in habitats where they have not raphy, and associated species–area relationships for been seen before, reports on invasive phytoplankton algae. species, and the increasing number of papers with phylogenetic trees and tracing secondary metabolites, Keywords Distribution Á Dispersal Á Invasion Á especially cyanotoxins, contradict. Phytoplankton Island biogeography Á Genomics Á Bloom-forming species, with rare exceptions, are neither cosmopoli- cyanobacteria tan, nor ubiquists. In this review paper,
    [Show full text]
  • Occurrence of a Cyanobacterial Neurotoxin, Anatoxin-A, in New
    OCCURRENCE OF THE CYANOBACTERIAL NEUROTOXIN, ANATOXIN-A, IN NEW YORK STATE WATERS by Xingye Yang A dissertation submitted in partial fulfillment of the requirements for the Doctor of Philosophy Degree State University of New York College of Environmental Science and Forestry Syracuse, New York January 2007 Approved: Faculty of Chemistry ---------------------------------------------- ------------------------------------------------ Gregory L. Boyer, Major Professor William Shields, Chairperson, Examination Committee ------------------------------------------------ ------------------------------------------------- John P. Hassett, Faculty Chair Dudley J. Raynal, Dean, Instruction and Graduate Studies UMI Number: 3290535 Copyright 2008 by Yang, Xingye All rights reserved. UMI Microform 3290535 Copyright 2008 by ProQuest Information and Learning Company. All rights reserved. This microform edition is protected against unauthorized copying under Title 17, United States Code. ProQuest Information and Learning Company 300 North Zeeb Road P.O. Box 1346 Ann Arbor, MI 48106-1346 Acknowledgements I would like to express my sincerest gratitude to Dr. Gregory L. Boyer, my major professor and academic advisor for his guidance, support, and assistance over the past years. He has provided me with invaluable knowledge and skills. I thank Dr. David J. Kieber for his advice and instrument support. I acknowledge Dr. John P. Hassett for his support on both my research and my career. I appreciate Dr. Francis X. Webster for his help on chemical characterization. I thank Dr. James P. Nakas for advice on my career development. Thanks are also due to Dr. William Shields for serving as chairman of this examination committee. I appreciate critical reviews and comments on the thesis from all the examiners on this committee. I would like to thank Dr. Israel Cabasso and Dr.
    [Show full text]
  • Recent Unusual Mean Winter Temperatures Across the Contiguous United States
    Recent Unusual Mean Winter Thomas R. Karl1, Robert E. Livezey2 Temperatures Across the Contiguous United States Abstract United States, even in an unusually cold (or warm) winter, can include a month of relatively mild (or cold) weather or A long-time series (1895-1984) of mean areally averaged winter contain small portions of the country that have relatively temperatures in the contiguous United States depicts an unprece- mild (or cold) weather throughout the winter. dented spell of abnormal winters beginning with the winter of 1975-76. Three winters during the eight-year period, 1975-76 through 1982-83, are defined as much warmer than normal (abnor- mal), and the three consecutive winters, 1976-77 through 1978-79, 2. Data much colder than normal (abnormal). Abnormal is defined here by the least abnormal of these six winters based on their normalized departures from the mean. When combined, these two abnormal The data set used to obtain areally weighted average winter categories have an expected frequency close to 21%. Assuming that temperature departures was originally used and described by the past 89 winters (1895-1984) are a large enough sample to esti- Diaz and Quayle (1978). The data, which begin in 1931, con- mate the true interannual temperature variability between winters, sist of monthly averages of temperatures for each of 344 state we find, using Monte Carlo simulations, that the return period of a series of six winters out of eight being either much above or much climatic divisions (CDs) in the contiguous United States, below normal is more than 1000 years.
    [Show full text]