Biology, Epidemiology and Management of Pyrodinium Red Tides

Total Page:16

File Type:pdf, Size:1020Kb

Biology, Epidemiology and Management of Pyrodinium Red Tides Biology, Epidemiology and Management of Pyrodinium Red Tides Edited by Gustaaf M. Hallegra~ff and Jay L. Maclean ~~~ , . ' ~ "', " ,;' . .. --,,'" , a,,",.:--,. ,~. "--="".~~ -~- '0 IJhology, Epidemiology and Management of Pyrodinium Red Tides Proceedings of the Management and Training Workshop Bandar Seri Begawan, Brunei Darussalam 23-30 May 1989 Edited by Gustaaf M. Hallegraeff an% J.L. Maclean FISHERIES DEPARTMENT, MINISTRY OF DEVELOPMENT BANDAR SERI BEGAWAN,BRUNEI DARUSSALAM INTERNATIONAL CENTER FOR LIVING AQUATIC RESOURCES MANAGEMENT MAN'ILA, PHILIPPINES Biology, epidemiology and management of Pyrodinium red tides Proceedings of the Management and Training Workshop Bandar Seri Begawan, Brunei Darussalam 23-30 May 1989 374 Edited by G.M. HALLEGRAEFF and J.L. MACLEAN Printed in Manila, Philippines Published by tlie Fisheries Department, Ministry of Development, P.O. Box 2161, Bandar Seri Begawan 1921, Brunei Darussalam, and International Center for Living Aquatic Resources Management, MC P.O. Box 1501, Makati, Metro Manila, Philippines Hallegraeff, G.M. and J.L. Maclean, Editors. 1989. Biology, epidemiology and management of Pyrodinium red tides. ICLARM Conf. hc.21,286 p. ISSN 0115-4435 ISBN 971 -1022-64-8 Cover: Electron micrograph of Pyrodinium bahamense bahamense, Oyster Bay, Jamaica, from a sample collected by R J.Buchanan on 17 March 1967. Photograph by Gustaaf Hallegraeff. ICLARM Contribution No. 585. Biology, Epidemiology and Management of Pyrodinium Red Tides Contents Foreword vi Preface viii Part 1. Proceedings of the Management and Training Workshop, Bandar Seri Begawan, Brunei Darussalam, 23 to 30 May 1989. Occurrences of red tides and paralytic shellfish poisoning An Overview of Pyrodinium red tides in the western Pacific. J.L. Maclean 1 Pyrodinium red tide occurrences in Brunei Darussalam. Matdanan Haji Jaafar, M.W.R.N. De Silva and P.H.Y. Sharifuddin 9 Summary of red tide and paralytic shellfish poisoning in St?bah, Malaysia. T.M.Ting and J.T.S. Wong 19 Red tides in Papua New Guinea waters. J.L. Maclean 27 Pyrodinium blooms and paralytic shellfish poisoning in the Philippines. C.L. Gonzales 39 The Guatemala? experience with red tides and paralytic shellfish poisoning. F. Rosales-hssener 49 Biology, Taxonomy, Toxicology Mechanisms for red tides of Pyrodinium bahamense var. compressum in Papua New Guinea, Sabah and Brunei Darussalam. H.H. Seliger 53 Toxins in Pyrodinium bahamense var. compressum and infested marine organisms. Y. Oshima 73 Cysts as factors in Pyrodinium ecology, D.M.Anderson 81 Occurrence of the cyst of Pyrodinium bahumense var. compressum in surface sediments of Brunei Bay. K. Matsuoka, Y. Fukuyo, Matdanan H. Jaafar and M. W.R.N.De Silva 89 Pyrodinium bahamense var. compressum red tide studies in Sabah, Malaysia. Gires Usup, Asmat Ahmad and Norhadi Ismail 97 Research, Monitoring and Equipment Research personnel and training needs (l'.Okaichi, J.L. Maclean) 111 Discussion and recommendations on research on the biology, ecology and toxicology (D.M. Anderson, G.M. Hallegraeff and J.L. Maclean) 115 Recommendations for Pyrodinium monitoring and research equipment (D.M. Anderson) 121 Management Management of Pyrodinium red tides in Brunei Darussalam. M.W.R.N. De Silva, A.H.M. Salleh, S.I. Mahali and S. Subramaniam 125 Management of red tides in Sabah, Malaysia. J.T.S. Wong and T.M. Ting 135 Management of toxic red tides in the Philippines. C.L. Gonzales 141 Management approaches to red tides in Papua New Guinea. K. Riroriro and L. D. Sims 149 Management of red tides and pazalytic shellfish poisoning in Guatemala. F. Rosales-Loessener 153 Methods of controlling Pyrodinium red tides. (T. Okaichi) 155 Monitoring principles. (G.M. Hallegraeff, S. Blackburn) 157 Discussions and recommendations on management issues. (T.E. Chua) 159 Epidemiology Epidemics of paralytic shellfish poisoning in the Philippines, 1988- 1989. N.I.S. Pastor, I. Gopez, M.C. Quizon, N. Bautista, M. White and M. Dayrit 165 Discussion on medical and epidemiologic issues. (N.Y.Pastor, R.A. Corrales) 173 Economics Economic aspects of Pyrodinium red tides in the western Pacific. J.L. Maclean 179 Discussion and recommendations on economic issues. (J.L. Maclean, 0. Ross) 187 List of Participants and Participation 189 Part 2. Manud for Field and Labomtory Research on the Dinoflagellate Pyrodinium bahamense Identification Morphological characteristics of dinoflagellates. Y. Fukuyo and F. J.R. Taylor 201 Morphological features of the motile cell of Pyrodinium bahamense. F. J.R. Taylor and Y. Fukuyo 207 Morphological features of the cyst of Pyrodinium bahamense var. compressum. K. Matsuoka 219 Methods for dinoflagellate cyst studies. (K. Matsuoka, Y. Fukuyo and D.M. Anderson) 231 Field Methodology Sampling coastal dinoflagellate blooms: equipment, strategies and data processing. P. J.S. Franks and D.M. Anderson 235 Laboratory Techniques Review of culture methods for Pyrodinium bahamense. S.I. Blackburn and Y. Oshima 257 Standard mouse bioassay for paralytic shellfish toxins. AOAC 267 Analysis of Pyrodinium bahamense PSP toxins by high-performance liquid chromatography. Y. Oshima 273 Epidemiology Guidelines in investigating PSP epidemics. N.I.S. Pastor, M.E. White and2ld.D. Dayrit 279 Foreword Red tide has become a frequent phenomenon in the coastal waters in many parts of the world. In Southeast Asia many lives have been lost and thousands taken ill from eating contaminated seafoods. Economic losses are also serious and effective mitigating measures are greatly needed. In 1984 two regional meetings, a WESTPAC Red Tide workshop at CSIRO in Cronulla (Australia) and a SEAFDEC/IDRC meeting on Toxic Red Tides and Shellfish Toxicity in Southeast Asia held in Singapore, unanimously declared Pyrodinium bahamense as the "number one" red tide danger in the Indo-West Pacific region. Urged by the 1987 Guatemala poisonings and the first appearance in 1988 of red tides in Manila Bay (Philippines), the concept of a meeting devoted exclusively to Pyrodinium bahamense was first proposed by Dr. Gustaaf M. Hallegraeff of CSIRO and Mr. J.L. Maclean of ICLARM. The ASEAN/US Coastal Area Management Project took up the proposal and developed it into a Pyrodinium red tide management and training workshop which permitted the participation of red tide researchers, public health officers and administrators to discuss research and management issues on Pyrodinium red tides and to develop a training manual. Brunei Darussalam readily hosted the workshop and contributed to part of local costs of the workshop. The idea found ready support from a number of donor agencies: The Australian International Development Assistance Bureau (AIDAB), the United Nations Environment Program (UNEP), Intergovernmental Oceanographic Commission (IOCIWESTPAC), the National Academy of Sciences, USA, International Development Research Centre (IDRC) of Canada and the United States Agency for International Development (USAID). As a result, from 23 to 30 May 1989, over 40 researchers from the six Asean countries (Brunei Darussalam, Indonesia, Malaysia, the Philippines, Singapore, Thailand), and from Australia, Canada, Japan, Papua New Guinea, Central America and the USA gathered in Brunei Darussalam to discuss the biological, economic, management, medical and training issues of Pyrodinium red tides. We were pleased that the workshop was successfully concluded and the proceedings published within a period of six months. Credit should be given to the enthusiasm and untiring efforts of Dr. Hallegraeff and Mr. Maclean as well as technical support staff of the Department of Fisheries, University of Brunei Darussalam and ICLARM. Haji Matdanan bin Jaafar Chua Thia Eng Director Project Coordinator Department of Fisheries ASEANNS Coastal Resources Brunei Darussalam Management Project, and Director Coastal Area Management Program, ICLARM vii Preface The dinoflagellate Pyrodinium bahamense Plate 1906 (Pyro = fire; bahamense = from the Bahamas) was first described from the tropical Atlantic more than 80 years ago. In Bahia Fosforescente in Puerto Rico and Oyster Bay in Jamaica, this species forms persistent luminescent blooms which are a major tourist attraction. Residents in these areas eat small oysters attached to mangrove roots, apparently without ill effects. The first harmful implications of Pyrodinium blooms became evident in 1972 in Papua New Guinea. Red-brown water discolorations coincided with the fatal food poisoning of three children and mouse bioassays on shellfish from a house in the affected village subsequently established Pyrodinium bahamense as the source of paralytic shellfish poisons. Since then, toxic Pyrodinium blooms have apparently spread to Brunei and Sabah (1976), the central Philippines (1983) and the northern Philippines (1987). Most unexpectedly, in 1987 on the Pacific coast of Guatemala, 187 people had to be hospitalized after consumption of toxic clams and 26 persons died. The problem was initially attributed to pesticide poisoning and only later linked to Pyrodinium. Altogether, this species has now been responsible for more than 1,000 human illnesses and 60 fatalities resulting from the consumption of contaminated shellfish as well as planktivorous fish such as sardines and anchovies. Unfortunately, the tropical countries in the Indo-West Pacific (Brunei, Indonesia, Palau, Papua New Guinea, Philippines, Sabah, Solomon Islands) and Latin America (Guatemala, Venezuela) that are affected (Fig. 1) depend heavily on seafoods for protein and have little prim experience in toxic dinoflagellate
Recommended publications
  • Sabah REDD+ Roadmap Is a Guidance to Press Forward the REDD+ Implementation in the State, in Line with the National Development
    Study on Economics of River Basin Management for Sustainable Development on Biodiversity and Ecosystems Conservation in Sabah (SDBEC) Final Report Contents P The roject for Develop for roject Chapter 1 Introduction ............................................................................................................. 1 1.1 Background of the Study .............................................................................................. 1 1.2 Objectives of the Study ................................................................................................ 1 1.3 Detailed Work Plan ...................................................................................................... 1 ing 1.4 Implementation Schedule ............................................................................................. 3 Inclusive 1.5 Expected Outputs ......................................................................................................... 4 Government for for Government Chapter 2 Rural Development and poverty in Sabah ........................................................... 5 2.1 Poverty in Sabah and Malaysia .................................................................................... 5 2.2 Policy and Institution for Rural Development and Poverty Eradication in Sabah ............................................................................................................................ 7 2.3 Issues in the Rural Development and Poverty Alleviation from Perspective of Bangladesh in Corporation City Biodiversity
    [Show full text]
  • Toxicity Equivalence Factors for Marine Biotoxins Associated with Bivalve Molluscs TECHNICAL PAPER
    JOINT FAO/WHO Toxicity Equivalency Factors for Marine Biotoxins Associated with Bivalve Molluscs TECHNICAL PAPER Cover photograph: © FAOemergencies JOINT FAO/WHO Toxicity equivalence factors for marine biotoxins associated with bivalve molluscs TECHNICAL PAPER FOOD AND AGRICULTURE ORGANIZATION OF THE UNITED NATIONS WORLD HEALTH ORGANIZATION ROME, 2016 Recommended citation: FAO/WHO. 2016. Technical paper on Toxicity Equivalency Factors for Marine Biotoxins Associated with Bivalve Molluscs. Rome. 108 pp. The designations employed and the presentation of material in this publication do not imply the expression of any opinion whatsoever on the part of the Food and Agriculture Organization of the United Nations (FAO) or of the World Health Organization (WHO) concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries. Dotted lines on maps represent approximate border lines for which there may not yet be full agreement. The mention of specific companies or products of manufacturers, whether or not these have been patented, does not imply that these are or have been endorsed or recommended by FAO or WHO in preference to others of a similar nature that are not mentioned. Errors and omissions excepted, the names of proprietary products are distinguished by initial capital letters. All reasonable precautions have been taken by FAO and WHO to verify the information contained in this publication. However, the published material is being distributed without warranty of any kind, either expressed or implied. The responsibility for the interpretation and use of the material lies with the reader. In no event shall FAO and WHO be liable for damages arising from its use.
    [Show full text]
  • Ecosystem Approach to Fisheries Management (EAFM) Country Position Paper—Malaysia
    CORAL TRIANGLE INITIATIVE: EcOSYSTEM APPROACH TO FISHERIES MANAGEMENT (EAFM) Country Position Paper—Malaysia May 2013 This publication was prepared for Malaysia’s National Coordinating Committee with funding from the United States Agency for International Development’s Coral Triangle Support Partnership (CTSP). Coral Triangle Initiative: Ecosystem Approach to Fisheries Management (EAFM): Country Position Paper – Malaysia AUTHOR: Kevin Hiew EDITOR: Jasmin Saad, OceanResearch KEY CONTRIBUTORS: Gopinath Nagarai, Fanli Marine Consultancy USAID PROJecT NUMBER: GCP LWA Award # LAG-A-00-99-00048-00 CITATION: Hiew, K., J. Saad, and N. Gopinath. Coral Triangle Initiative: Ecosystem Approach to Fisheries Management (EAFM): Country Position Paper—Malaysia. Publication. Honolulu, Hawaii: The USAID Coral Triangle Support Partnership, 2012. Print. PRINTED IN: Honolulu, Hawaii, May 2013 This is a publication of the Coral Triangle Initiative on Corals, Fisheries and Food Security (CTI-CFF). Funding for the preparation of this document was provided by the USAID-funded Coral Triangle Support Partnership (CTSP). CTSP is a consortium led by the World Wildlife Fund, The Nature Conservancy and Conservation International with funding support from the United States Agency for International Development’s Regional Asia Program. For more information on the Coral Triangle Initiative, please contact: Coral Triangle Initiative on Coral Reefs, Fisheries and Food Security Interim-Regional Secretariat Ministry of Marine Affairs and Fisheries of the Republic of Indonesia Mina Bahari Building II, 17th Floor Jalan Medan Merdeka Timur No. 16 Jakarta Pusat 10110, Indonesia www.coraltriangleinitiative.org CTI-CFF National Coordinating Committee Professor Nor Aeni Haji Mokhtar Under Secretary National Oceanography Directorate, Ministry of Science, Technology and Innovation, Level 6, Block C4, Complex C, Federal Government Administrative Centre, 62662 Putrajaya, Malaysia.
    [Show full text]
  • 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
    [Show full text]
  • Guanidinium Toxins and Their Interactions with Voltage-Gated Sodium Ion Channels
    marine drugs Review Guanidinium Toxins and Their Interactions with Voltage-Gated Sodium Ion Channels Lorena M. Durán-Riveroll 1,* and Allan D. Cembella 2 ID 1 CONACYT—Instituto de Ciencias del Mary Limnología, Universidad Nacional Autónoma de México, Mexico 04510, Mexico 2 Alfred-Wegener-Institut, Helmholtz Zentrum für Polar-und Meeresforschung, 27570 Bremerhaven, Germany; [email protected] * Correspondence: [email protected]; Tel.: +52-55-5623-0222 (ext. 44639) Received: 29 June 2017; Accepted: 27 September 2017; Published: 13 October 2017 Abstract: Guanidinium toxins, such as saxitoxin (STX), tetrodotoxin (TTX) and their analogs, are naturally occurring alkaloids with divergent evolutionary origins and biogeographical distribution, but which share the common chemical feature of guanidinium moieties. These guanidinium groups confer high biological activity with high affinity and ion flux blockage capacity for voltage-gated sodium channels (NaV). Members of the STX group, known collectively as paralytic shellfish toxins (PSTs), are produced among three genera of marine dinoflagellates and about a dozen genera of primarily freshwater or brackish water cyanobacteria. In contrast, toxins of the TTX group occur mainly in macrozoa, particularly among puffer fish, several species of marine invertebrates and a few terrestrial amphibians. In the case of TTX and analogs, most evidence suggests that symbiotic bacteria are the origin of the toxins, although endogenous biosynthesis independent from bacteria has not been excluded. The evolutionary origin of the biosynthetic genes for STX and analogs in dinoflagellates and cyanobacteria remains elusive. These highly potent molecules have been the subject of intensive research since the latter half of the past century; first to study the mode of action of their toxigenicity, and later as tools to characterize the role and structure of NaV channels, and finally as therapeutics.
    [Show full text]
  • Ecological Characterization of Bioluminescence in Mangrove Lagoon, Salt River Bay, St. Croix, USVI
    Ecological Characterization of Bioluminescence in Mangrove Lagoon, Salt River Bay, St. Croix, USVI James L. Pinckney (PI)* Dianne I. Greenfield Claudia Benitez-Nelson Richard Long Michelle Zimberlin University of South Carolina Chad S. Lane Paula Reidhaar Carmelo Tomas University of North Carolina - Wilmington Bernard Castillo Kynoch Reale-Munroe Marcia Taylor University of the Virgin Islands David Goldstein Zandy Hillis-Starr National Park Service, Salt River Bay NHP & EP 01 January 2013 – 31 December 2013 Duration: 1 year * Contact Information Marine Science Program and Department of Biological Sciences University of South Carolina Columbia, SC 29208 (803) 777-7133 phone (803) 777-4002 fax [email protected] email 1 TABLE OF CONTENTS INTRODUCTION ............................................................................................................................................... 4 BACKGROUND: BIOLUMINESCENT DINOFLAGELLATES IN CARIBBEAN WATERS ............................................... 9 PROJECT OBJECTIVES ..................................................................................................................................... 19 OBJECTIVE I. CONFIRM THE IDENTIY OF THE BIOLUMINESCENT DINOFLAGELLATE(S) AND DOMINANT PHYTOPLANKTON SPECIES IN MANGROVE LAGOON ........................................................................ 22 OBJECTIVE II. COLLECT MEASUREMENTS OF BASIC WATER QUALITY PARAMETERS (E.G., TEMPERATURE, SALINITY, DISSOLVED O2, TURBIDITY, PH, IRRADIANCE, DISSOLVED NUTRIENTS) FOR CORRELATION WITH PHYTOPLANKTON
    [Show full text]
  • Development and Validation of a Novel Approach for the Analysis of Marine Biotoxins
    DEVELOPMENT AND VALIDATION OF A NOVEL APPROACH FOR THE ANALYSIS OF MARINE BIOTOXINS Bing Cheng Chai College of Engineering and Science Victoria University Submitted in fulfilment of the requirements of the degree of Doctor of Philosophy June 2017 ABSTRACT Harmful algal blooms (HABs) which can produce a variety of marine biotoxins are a prevalent and growing risk to public safety. The aim of this research was to investigate, evaluate, develop and validate an analytical method for the detection and quantitation of five important groups of marine biotoxins in shellfish tissue. These groups included paralytic shellfish toxins (PST), amnesic shellfish toxins (AST), diarrheic shellfish toxins (DST), azaspiracids (AZA) and neurotoxic shellfish toxins (NST). A novel tandem liquid chromatographic (LC) approach using hydrophilic interaction chromatography (HILIC), aqueous normal phase (ANP), reversed phase (RP) chromatography, tandem mass spectrometry (MSMS) and fluorescence spectroscopic detection (FLD) was designed and tested. During method development of the tandem LC setup, it was found that HILIC and ANP columns were unsuitable for the PSTs because of the lack of chromatographic separation power, precluding them from being used with MSMS detection. In addition, sensitivity for the PSTs at regulatory limits could not be achieved with MSMS detection, which led to a RP-FLD combination. The technique of RP-MSMS was found to be suitable for the remaining four groups of biotoxins. The final method was a combination of two RP columns coupled with FLD and MSMS detectors, with a valve switching program and injection program. A novel sample preparation method was also developed for the extraction and clean-up of biotoxins from mussels.
    [Show full text]
  • Paralytic Shellfish Poisoning Toxins: Biochemistry and Origin
    Aqua-BioScience Monographs Vol. 3, No. 1, pp. 1–38 (2010) www.terrapub.co.jp/onlinemonographs/absm/ Paralytic Shellfish Poisoning Toxins: Biochemistry and Origin Masaaki Kodama Laboratory of Marine Biochemistry, Department of Aquatic Biosciences, Graduate School of Agricultural and Life Sciences, The University of Tokyo 1-1-1 Yayoi, Bunkyo, Tokyo 113-8657, Japan e-mail: [email protected] Abstract Plankton feeders such as bivalves often become toxic. Human consumption of the toxic bivalve Received on September 8, 2009 causes severe food poisoning, including paralytic shellfish poisoning (PSP) which is the most Accepted on October 13, 2009 dangerous because of the acuteness of the symptoms, high fatality and wide distribution throughout Published online on the world. Accumulation of PSP toxins in shellfish has posed serious problems to public health April 9, 2010 and fisheries industry. The causative organisms of PSP toxins are known to be species of dinoflagellates including those belonging to the genus Alexandrium, Gymnodinium catenatum Keywords and Pyrodinium bahamense var. compressum. Bivalves accumulate PSP toxins during a bloom • paralytic shellfish poisoning toxins of these dinoflagellates. Thus, the dinoflagellate toxins have been considered as being concen- • saxitoxin trated in bivalves through food web transfer. However, field studies on the toxin level of bivalves • gonyautoxin in association with the abundance of toxic dinoflagellates could not support the idea. A kinetics • tetrodotoxin study on toxins by feeding experiments of cultured dinoflagellate cells to bivalves also showed • dinoflagellate similar results, indicating that toxin accumulation of bivalves is not caused by simple accumula- • Alexandrium tamarense tion of toxins due to food-web transfer.
    [Show full text]
  • Harmful Algal Blooms (Habs) and Desalination: a Guide to Impacts, Monitoring and Management; IOC. Manuals and Guides; Vol.:78; 2
    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 Removal of algal toxins and taste and odor compounds 10 REMOVAL OF ALGAL TOXINS AND TASTE AND ODOR COMPOUNDS DURING DESALINATION Mike B. Dixon1, Siobhan F.E. Boerlage2, Holly Churman3, Lisa Henthorne3, and Donald M. Anderson4 1 MDD Consulting, Kensington, Calgary, Alberta, Canada 2 Boerlage Consulting, Gold Coast, Queensland, Australia 3Water Standard, Houston, Texas, USA 4Woods Hole Oceanographic Institution,Woods Hole MA USA 10.1 Introduction ......................................................................................................................................... 315 10.2 Chlorination ......................................................................................................................................... 316 10.3 Dissolved air flotation (DAF) ............................................................................................................
    [Show full text]
  • A Study on Tuaran River Channel Planform and the Effect of Sand Extraction on River Bed Sediments
    Transactions on Science and Technology Vol. 4, No. 4, 442 - 448, 2017 A Study on Tuaran River Channel Planform and the Effect of Sand Extraction on River Bed Sediments Jayawati Montoi1#, Siti Rahayu Mohd. Hashim2, Sanudin Tahir1 1 Geology Programme, Faculty of Science and Natural Resources, Universiti Malaysia Sabah, Jalan UMS, 88400 Kota Kinabalu, Sabah, MALAYSIA. 2 Mathematic With Economic Programme, Faculty of Science and Natural Resources, Universiti Malaysia Sabah, Jalan UMS, 88400 Kota Kinabalu, Sabah, MALAYSIA. # Corresponding author. E-Mail: [email protected]; Tel: +6088-260311; Fax: +6088-240150. ABSTRACT River sand extraction is known as one of the main factors that induces the significant changes on river planform. This paper main objective is to study on the significance of planform changes on Tuaran River from 2003 to 2016 and sediment composition changes due to this activity. The study on channel planform focuses on four single wavelength channel bends which are located at the downstream of Tuaran River. Two meander features which are the channel width (w) and radius of curvature (Rc) were measured from digitized Google Earth satellite image year 2003, 2013, 2014 and 2016 and overlay with the Department of Survey and Mapping Malaysia (JUPEM) topographic map using Geographic Information System (GIS) software and georeferenced to World Geodetic System (WGS) 1984. Four sites which are located at the downstream of Tuaran River were selected to determine the river bed sediments composition. Three of the four sites are located at the sand extraction area whilst one site is a controlled area with no sand extraction activity. River bed sediments were collected and the sediments composition was analyzed using Mann Whitney and Kruskal-Wallis tests to determine the composition difference between the areas and the inner parts of the river.
    [Show full text]
  • Cyanobacterial Toxins: Saxitoxins
    WHO/HEP/ECH/WSH/2020.8 Cyanobacterial toxins: saxitoxins Background document for development of WHO Guidelines for Drinking-water Quality and Guidelines for Safe Recreational Water Environments WHO/HEP/ECH/WSH/2020.8 © World Health Organization 2020 Some rights reserved. This work is available under the Creative Commons Attribution- NonCommercial-ShareAlike 3.0 IGO licence (CC BY-NC-SA 3.0 IGO; https://creativecommons.org/ licenses/by-nc-sa/3.0/igo). Under the terms of this licence, you may copy, redistribute and adapt the work for non-commercial purposes, provided the work is appropriately cited, as indicated below. In any use of this work, there should be no suggestion that WHO endorses any specific organization, products or services. The use of the WHO logo is not permitted. If you adapt the work, then you must license your work under the same or equivalent Creative Commons licence. If you create a translation of this work, you should add the following disclaimer along with the suggested citation: “This translation was not created by the World Health Organization (WHO). WHO is not responsible for the content or accuracy of this translation. The original English edition shall be the binding and authentic edition”. Any mediation relating to disputes arising under the licence shall be conducted in accordance with the mediation rules of the World Intellectual Property Organization (http://www.wipo.int/amc/en/ mediation/rules/). Suggested citation. Cyanobacterial toxins: saxitoxins. Background document for development of WHO Guidelines for drinking-water quality and Guidelines for safe recreational water environments. Geneva: World Health Organization; 2020 (WHO/HEP/ECH/WSH/2020.8).
    [Show full text]
  • Jica Report.Pdf
    ISBN: 978-983-3108-23-7 Report of Economics of River Basin Management fer Sustainable Development for Biodiversity and Ecosystems Conservation in Sabah Copyright©2015 SDBEC Secretariat Editor: SDBEC Secretariat Published by: SDBEC Secretariat c/o Natural Resources Office 14th Floor, Menara Tun Mustapha 88502 Kota Kinabalu, Sabah, Malaysia TEL:088-422-120 FAX:088-422-129 Printed by: Infinity Graphics Print Sdn. Bhd. *Back cover photo credit to Mr. Awg. Shaminan Dtk. Hj. Awg. Sahari Preface In Sabah, around 53% of the total state land is designated as protected area or conservation site within which human activities are strictly regulated. A large scale plantation industry has been put in place and population growth has been the threats for natural resources around and near the border of protected area and conservation site. There have been increasing needs to develop new incentive mechanism for the better natural resource management. In the meantime, regardless of rapid economic development in Malaysia, Sabah is still suffering from poverty. Most of the needy people live in the mountainous area, thus rural development for poverty eradication is essential for human well-being. Sabah needs to pursue way toward a society in harmony with nature where harmonization between conservation and development can be realized. Sabah has some outstanding management systems like land-use control and environment awareness programme (Environmental Education). In order to promote environment-friendly and sustainable development more, integrated and innovative approaches are indispensable. Considering the above-mentioned matters, IlCA-SDBEC conducted the study on "Economics of River Basin Management for Sustainable Development for Biodiversity and Ecosystems Conservation" from December 2014 to February 2015.
    [Show full text]