Environmental Health Criteria 116 Tributyltin Compounds

Total Page:16

File Type:pdf, Size:1020Kb

Environmental Health Criteria 116 Tributyltin Compounds INTERNATIONAL PROGRAMME ON CHEMICAL SAFETY Environmental Health Criteria 116 Tributyltin Compounds Published under the joint sponsorship of the United Nations Environment Programme, the International Labour Organisation, and the World Health Organization H-. L1 Other titles available in the ENVIRONMENTAL HEALTH CRITERIA series include: 1. Me rcurya 37. Aquatic (Marine and 2. Polychlorinated Biphenyis and Freshwater) Biotoxins Terphenyls 38. Heptachlor 3. Leada 39. Paraquat and Diquat 4. Oxides of Nitrogen a 40. Endosulfan 5. Nitrates, Nitrites, and Quintozene iV-Nitroso Compo u ndsa Tecnaze.ne 6. Principles and Methods for Chlordecone Evaluating the Toxicity of Mirex Chemicals, Part 1 Camphechlor 7. Photochernjcal Oxidants 46. Guidelines for the Study of 8. Sulfur Oxides and Suspended Genetic Effects in Human Particulate Matter Populations 9. DDT and its Derivatives 47. Summary Report on the 10. Carbon Disulfide Evaluation of Short-term 'los II. Mycotoxins for Carcinogens (Collaborats 12. Noise Study on In Vitro Tests) 13. Carbon Monoxide 48. Dimethvl Sulfate 14. Ultraviolet Radiation 49. Acrylamide 15. Tin and Organotin Compounds 50. Trichloroethvlene 16. Radiofrequencv and Microwaves 51. Guide to Short-term Tests fo 17. Manganese Detecting Mutagenic and 18. Arsenic Carcinogenic Chemicals 19. Hydrogen Sulfide 52. Toluene 20. Selected Petroleum Products 53. Asbestos and Other Natural 21. Chlorine and Hydrogen Mineral Fibres Chloride 54. Ammonia 22. Ultrasound 55, Ethylene Oxide 23. Lasers and Optical Radiation 56. Propylene Oxide 24. Titanium 57. Principles of Toxicokinetic 25. Selected R ad ion eel ides Studies 26. Styrene 58. Selenium 27. Guidelines on Studies in 59. Principles for Evaluating Environmental Epidemiology Health Risks from Chemicals 28. Acrvlonitrile During Infancy and Early 29. 24-Dichlorophenoxvacetic Childhood: The Need for a Acid (2,4-D) Special Approach 30. Principles for Esaluating 60. Principles and Methods for 0 Health Risks to Progeny Assessment of Neurotoxicit\ Associated with Exposure to Associated With Exposure to Chemicals during Pregnancs Chemicals 31. 'letrachloroethylene 61. Chromium 32. Methytene Chloride 62. 1,2-Dichloroethane 33. Epichlorohvdrin 63. Organophosphorus Insecticide 34. Chlorclane - A General Introduction 35. Extremely Low Frequency 64. Carhamate Pesticides - (ELF) Fields A General Introduction 36. Fluorine and Fluorids 65. Butanols - Four Isomers Out of print ('(nH fl.'d iii iiJ' 15(11k ('(In', This regal t conta its the collective iesvs of an in- lernational group of experts and does not neccsarilv represent the decisions or the stated polics of the lJniied Nations Luvironmen! Prograinnie, the Interna- tional Iahoui Organisation. or the World I lealth 0 roam in t o it Environmental Health Criteria 116 TRIBUTYLTIN COMPOUNDS Published under the joint sponsorship of the [nited Nations Environment Programme, the International Labour Organisation, and the World Health Organization I irst dra ft preparer! by Dr S. Dobson. Institute at Terrestrial Eeolortv. United kingdom. and L)r R. (labridene, lnstitnt National ne Recherche Cliinnque Appliqude, Fiance World Health Organization Geneva, 1990 The International Programme on Chemical Safety (IPCS) is a jo nt venture of the United Nations Environment Programme, the Internatiot al Labour Organisation, and the World Health Organization. The main obje tive of the IPCS is to carry out and disseminate evaluations of I ie effects of chemicals on human health and the quality of the env,roo- ment. Supporting activities include the development of epiderniologic:sl. experimental laborator, and risk-assessment methods that could prodLce internationally comparable results, and the development of manpower in the field of toxicology. Other acti ties carried out by the lPS include the development of know-how for coping with chemical accidents. coordination of laboratory testing a n d epidemiological studies, a i d promotion of research on the mechanisms of the biological action of o he mica Is. WHO Library Cataloguing in Publication Data Trihutyltin compounds. (Environmental health criteria 116) 1. Trialkyltin compounds - adverse effects 2. Trialkvltin compounds - toxicity 1. Series ISBN 92 4 157116 0 (NI.M Classification: QV 290) ISSN 0250-863X ©World Health Organization 1990 Publications of the World health Organization enjoy copyright pro- tection in accordance with the provisions of Protocol 2 of the Unive- sal Copyright Convention. For rights of reproduction or translation )f WHO publications, in part or in low, application should be made to tie Office of Publications. World Health Organization, Geneva, Switzerlari The World Health Organization welcomes such applications. The designations employed and the presentation of the material n this publication do not imply the expression of ans opinion whatsoe\ r on the part of the Secretariat of the World Health Organization coo- cerning the legal status of an countr\ territory, city. or area or its authorities, or concerning the delimitation of its frontiers ,r boundaries. Ihe mention of specific companies or of certain manufacture:s' products does not impis that they are endorsed or recommended by tie World Health Organization in preference to others of a similar nature that are not mentioned. Errors and omissions excepted, the names )f proprietary products are distinguished by initial capital letters. H \ininH EHC 116: Tributyltin Compounds CONTENTS ENVIRONMENTAL HEALTH CRITERIA FOR TRIBUTYLTIN COMPOUNDS SUMMARY 13 1.1 Physical and chemical properties 13 1.2 Analytical methods 13 1.3 Sources of environmental pollution 14 1.4 Regulations on use 14 1.5 Environmental concentrations 14 1.6 Transport and transformation in the environment 15 1.7 Kinetics and metabolism 16 1.8 Effects on microorganisms 17 1.9 Effects on aquatic organisms 17 1.9.1 Effects on marine and estuarine organisms 17 1.9.2 Effects on freshwater organisms 19 1.9.3 Microcosm studies 21 1.10 Effects on terrestrial organisms 22 1.11 Effects on organisms in the field 1.12 Toxicity to laboratory mammals 23 1.12.1 Acute toxicity 23 1.12.2 Short-term toxicity 23 1.12.3 Long-term toxicity 26 1.12.4 Genotoxicity 26 1.12.5 Reproductive toxicity 26 .12.6 Carcinogenicity 1.13 Effects on humans 7 IDENTITY, PHYSICAL AND CHEMICAL PROPERTIES, ANALYTICAL METHODS 28 2.1 Identity of tributyltin compounds 28 2.2 Physical and chemical properties 28 2.3 Analytical methods 31 2.3.1 Measurement of organotin compounds 31 2.3.1.1 Extraction of tributyltin derivatives -'.1, 2.3.1.2 Formation of volatile derivatives 33 2.3.1.3 Separation of organotin derivatives -'3 2.3.1.4 Detection and measurement of different forms of organotin 34 tj 2.3.2 Interlaboratory calibrations 34 SOURCES OF ENVIRONMENTAL EXPOSURE 36 3.1 Uses 36 3.2 Production 37 3.3 Regulations 38 ENVIRONMENTAL TRANSPORT AND TRANSFORMATION 4.1 Adsorption onto and desorption from particles 43 4.2 Abiotic degradation 45 4.2.1 Hydrolytic cleavage of the tin-carbon bond 46 4.2.2 Photodegradation 47 4.3 Biodegradation 48 4.4 Bioaccumulation and elimination 52 ENVTRONMETAL CONCENTRATIONS 5.1 Sea water and marine sediment 5.2 Fresh water and sediment 61 5.3 Sewage treatment 64 5.4 Biota 64 KINETICS AND METABOLISM 70 6.1 Metabolism of TBT in mammals 70 6.2 Metabolism of TBTO in other organisms 73 6.3 General mechanisms of toxicity of TBTO 74 6.3.1 General toxic mechanisms 74 6.3.2 Toxic mechanisms in bivalve molluscs 7-1 EFFECTS ON ORGANISMS IN THE ENVIRONMENT: MICROORGANISMS 76 7.1 Bacteria and fungi 76 7.2 Freshwater algae 78 7.3 Estuarine and marine algae 79 EFFECTS ON ORGANISMS IN THE ENVIRONMENT: AQUATIC ORGANISMS 8.1 Aquatic plants 82 4 EHC 116: Tributyltin Compounds 8.2 Aquatic invertebrates 83 8.2.1 Trematode parasites of man 83 8.2,2 Freshwater molluscs 87 8.2.2.1 Acute toxicity 88 8.2.2.2 Short- and long-term toxicity 89 8.2.2.3 Factors affecting toxicity 90 8.2.3 Marine molluscs 92 8.2.3.1 Acute toxicity 93 8.2.3.2 Short- and long-term toxicity 93 8,2.3.3 Reproductive effects 97 8.2.3.4 Effects on growth 98 8.2.3.5 Shell thickening 101 8.2.3,6 Imposex 101 8.2.3.7 Genotoxicity 106 8.2.4 Crustaceans 106 8.2.4.1 Acute effects 106 8.2.4.2 Short- and long-term toxicity 107 8.2.4.3 Reproductive effects 110 8.2.4.4 Limb regeneration Ill 8.2.4.5 Behavioural effects Ill 8.2.5 Other aquatic invertebrates 112 8.2.5.1 Acute effects 112 8.2.5,2 Limb regeneration 113 8.3 Fish 114 8.3.1 Acute effects 114 8.3.2 Short- and long-term toxicity 115 8.3.3 Embryotoxicity 121 8.3.4 Behavioural effects 122 8.4 Amphibians 123 8.5 Mulrispecies studies 124 EFFECTS ON ORGANISMS IN THE ENVIRONMENT: TERRESTRIAL ORGANISMS 129 9,1 Microcosm studies 129 9.2 Terrestrial insects 129 9.3 Terrestrial mammals 130 EFFECTS ON ORGANISMS IN THE ENVIRONMENT: FIELD OBSERVATIONS 132 10.1 Effects on bivalves 132 10.2 Effects on gastropods: imposex 138 10.3 Effects on farmed fish 142 10.4 Effects of TBT-contaminated sediment 143 10.5 Effects of freshwater molluscicides 144 10.6 Effects from spills 146 10.7 The use of indicator species for monitoring the environment 146 H. EFFECTS ON EXPERIMENTAL ANIMALS AND IN ViTRO TEST SYSTEMS 148 11.1 Single exposure 148 11.1.1 Oral and parenteral administration 148 11.1.2 Dermal administration 152 11.1.3 Administration by inhalation 153 II .1.4 Irritation and sensitization 154 11.1.4.1 Skin irritation 154 11.1.4.2 Eye irritation 156 11.1.4.3 Skin sensitization 157 11.1.5 In vitro studies 157 11.2 Short-term toxicity 160 11.2.1 Oral dosing: general body effects 163 11.2.2 Inhalation studies 164 11.2.3 Histopathological effects 165 11.2.4 Haematological and biochemical effects 166 11.2.5 Effects on lymphoid organs and immune function 167 11.2.6 Mechanism of immunotoxicity 178 11.2.7 Effects on the endocrine system 179 11.3 Long-term toxicity 180 11.4 Genotoxicity 181 11.5 Reproductive toxicity 184 11.5.1 In vivo 184 11.5.2 in vitro 187 11.6 Carcinogenicity 188 12.
Recommended publications
  • Ambient Aquatic Life Water Quality Criteria for Tributyltin (TBT) - Final AMBIENT AQUATIC LIFE WATER QUALITY CRITERIA FOR
    United States Office of Water EPA 822-R-03-031 Environmental Protection 4304T December 2003 Agency Ambient Aquatic Life Water Quality Criteria for Tributyltin (TBT) - Final AMBIENT AQUATIC LIFE WATER QUALITY CRITERIA FOR TRIBUTYLTIN CAS Registry Number (See Text) December 2003 U.S. ENVIRONMENTAL PROTECTION AGENCY OFFICE OF WATER OFFICE OF SCIENCE AND TECHNOLOGY HEALTH AND ECOLOGICAL CRITERIA DIVISION WASHINGTON D.C. NOTICES This document has been reviewed by the Health and Ecological Criteria Division, Office of Science and Technology, U.S. Environmental Protection Agency, and is approved for publication. Mention of trade names or commercial products does not constitute endorsement or recommendation for use. This document is available to the public through the National Technical Information Service (NTIS), 5285 Port Royal Road, Springfield, VA 22161. It is also available on EPA’s web site: http://www.epa.gov./waterscience/criteria/tributyltin. ii FOREWORD Section 304(a)(1) of the Clean Water Act of 1977 (P.L. 95-217) requires the Administrator of the Environmental Protection Agency 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. This final document is a revision of proposed criteria based upon consideration of scientific input received from U.S. EPA staff, the public and independent peer reviewers. Criteria contained in this document replace any previously published EPA aquatic life criteria for tributyltin (TBT). The term "water quality criteria" is used in two sections of the Clean Water Act, section 304(a)(1) and section 303(c)(2).
    [Show full text]
  • Evolution of Antifouling Paints
    International Journal of Science and Research (IJSR) ISSN (Online): 2319-7064 Index Copernicus Value (2015): 78.96 | Impact Factor (2015): 6.391 Evolution of Antifouling Paints Abdullah Saif Qureshi, Dr. Rajan Ramaswamy 1, 2Birla Institute of Technology and Science, Pilani- Dubai Campus, Academic City Road, Academic City, Dubai, U.A.E Abstract: Anti-fouling paints have been around us for decades. Ever since the discovery of Anti-fouling paints there has been a large development in the composition of the paint and its diverse effect on marine life. This project helps us study the history of anti-fouling paints, its evolution, reason for evolution, effect on marine life and also its future scope. Keywords: Antifouling Paints, Antifouling Systems, Biofouling, Marine life 1. Introduction 1.2.3 Why do ships need anti-fouling systems? Just a small amount of fouling can lead to an increase of fuel 1.1.1 What are Anti-fouling Paints? consumption of up to 40%, and possibly as much as 50%, As defined by Wikipedia, Anti-fouling paint is a category of since the resistance to movement will be increased. A clean commercially available underwater hull paints (also known ship can sail faster and with less energy. as bottom paints). It is a specialized category of coatings applied as the outer (outboard) layer to the hull of a ship or 1.2.4 How do anti-fouling systems save a ship owner boat, to slow the growth and/or facilitate detachment money? of subaquatic organisms that attach to the hull and can affect An effective anti-fouling system can save a shipowner money a vessel's performance and durability.
    [Show full text]
  • (12) United States Patent (10) Patent No.: US 9,580,608 B1 Denton Et Al
    USOO958.0608B1 (12) United States Patent (10) Patent No.: US 9,580,608 B1 Denton et al. (45) Date of Patent: Feb. 28, 2017 (54) SWITCHABLE ANTIFOULING COATINGS Eshet, I. et al., “Chemical and Physical Factors in Design of AND USES THEREOF Antibiofouling Polymer Coatings.” Biomacromolecules (2011) pp. 2681-2685, 12. Graham, M.V. et al., “Development of antifouling surfaces to reduce (71) Applicant: Sandia Corporation, Albuququerque, bacterial attachment.” Soft Matter (2013) pp. 6235-6244, 9. NM (US) Johnson, R.S. et al., “Thermally Induced Failure of Polymer Dielec trics.” Adv. Mater. (2010) pp. 1750-1753, 22. (72) Inventors: Michele L. Baca Denton, Bosque, NM Johnson, R.S. et al., “Photopatterning poly(p-phenylenevinylene) from Xanthate precursor polymers,” Chem. Commun. (2011) pp. (US); Shawn M. Dirk, Albuquerque, 3936-3938, 47. NM (US); Ross Stefan Johnson, Johnson, R.S. et al., “Photolithographic patterning of alkoxy sub Wilmington, DE (US) stituted poly(p-phenylenevinylene)s from Xanthate precursors,” J. Mater. Chem. C (2013) pp. 1428-1433, 1. (73) Assignee: Sandia Corporation, Albuquerque, NM Johnson, R.S. et al., “Thermally-Activated Pentanol Delivery from Precursor Poly(p-phenylenevinylene)s for MEMS Lubrication.” (US) Macromol. Rapid Commun. (2012) pp. 1346-1350, 33. Kanazawa, A. et al., “Novel Polycationic Biocides: Synthesis and (*) Notice: Subject to any disclaimer, the term of this Antibacterial Activity of Polymeric Phosphonium Salts.” J. Polym. patent is extended or adjusted under 35 Sci. Part A: Polym. Chem. (1993) pp. 335-343, 31. U.S.C. 154(b) by 21 days. Kanazawa, A. et al., “Antibacterial Activity of Polymeric Sulfonium Salts.” J.
    [Show full text]
  • Is the Writing on the Wall for Copper-Based Antifouling Paint? Part I: Introduction and Overview Part I
    White paper 7.qxp 21-10-2011 11:39 Pagina 1 WHITE PAPER Is the Writing on the Wall for Copper-based Antifouling Paint? HYDREX WHITE PAPER N°7 A close look at restrictions and legislation on copper and co-biocide based anti-fouling paints and a comparison with the cycle which led to the eventual ban of TBT The Hydrex Group www.hydrex.be White paper 7.qxp 21-10-2011 11:39 Pagina 2 ©Copyright 2011 by Hydrex, nv. All rights reserved. White paper 7.qxp 21-10-2011 11:39 Pagina 1 Is the Writing on the Wall for Copper-based Antifouling Paint? Part I: Introduction and overview Part I. Introduction and overview ntifouling paint based on Tributyltin use of TBT in antifouling paint on a local A(TBT) was developed in the 1960s, was level. widely available in the USA and Canada It was not until 2001 that legislation to towards the end of that decade, and was in ban TBT globally was agreed at the Inter- general use around the world in the 1970s, national Convention on the Control of 1980s and 1990s and into the first decade of Harmful Anti-fouling Systems on Ships the 21st century. (AFS) of the International Marine Organi- zation (IMO). Already by the late 1960s scientists were The eventual ban was to go into effect in aware of the negative impact of TBT on non- January 2003. It mandated that by 2008 ships target organisms, and its dangers to the must either bear no organotin compounds on marine environment and the food chain.
    [Show full text]
  • Stable Fluorinated Antimicrobial Coatings
    Virginia Commonwealth University VCU Scholars Compass Theses and Dissertations Graduate School 2012 Stable Fluorinated Antimicrobial Coatings Asima Chakravorty Virginia Commonwealth University Follow this and additional works at: https://scholarscompass.vcu.edu/etd Part of the Engineering Commons © The Author Downloaded from https://scholarscompass.vcu.edu/etd/450 This Dissertation is brought to you for free and open access by the Graduate School at VCU Scholars Compass. It has been accepted for inclusion in Theses and Dissertations by an authorized administrator of VCU Scholars Compass. For more information, please contact [email protected]. Stable Fluorinated Antimicrobial Coatings A dissertation submitted in partial fulfillment of the requirement for the degree of Doctor of Philosophy at Virginia Commonwealth University by ASIMA CHAKRAVORTY B.TECH (1999), Calcutta University, India B.Sc (Chemisrty) (1996) Calcutta University, India Director: Kenneth J. Wynne, Ph.D. Professor, Department of Chemical and Life Science Engineering Virginia Commonwealth University Richmond, VA December 2012 ACKNOWLEDGEMENTS The author wishes to thank all the people without whose support and understanding this journey would not have been possible. I would like to convey my gratitude to my advisor, Dr Kenneth Wynne for his continuous guidance and support. His constant encouragement and belief in me has helped me overcome the challenges I have faced in my research. I have learnt a lot from him and hope to make him proud in my future endeavors. I would also take this opportunity to thank all members of the Wynne group for their help and cooperation. Their friendship has made the last few years some of the best years of my life.
    [Show full text]
  • Mollusca, Gastropoda): Imposex Response and Consequences Along the Pakistan Coast During the Period from 1993 to 2012
    Afsar et al.: Bioindicator, Thais carinifera ORIGINAL ARTICLE / ARTIGO ORIGINAL BJOCE Bioindicator Thais carinifera (mollusca, gastropoda): imposex response and consequences along the Pakistan coast during the period from 1993 to 2012 Nuzhat Afsar*, Ghazala Siddiqui, Zarrien Ayub Center of Excellence in Marine Biology (CEMB), University of Karachi (UOK) (Karachi 75270, Pakistan) *Corresponding author: [email protected] ABSTRACT RESUMO Endocrine mediated "imposex" phenomenon was O fenômeno hormonal “imposex” foi investigado e investigated and recorded in the muricoid gastropod relatado para o gastrópode muricídeo Thais carinifera species Thais carinifera during the two decades from durante duas décadas, de 1993 a 2012, em três das 1993 to 2012 at three (3) sites out of six (6) localities seis localidades investigadas ao longo da costa de investigated along the Sindh and Balochistan coast, Sindh and Balochistão, Paquistão. Os estágios VDS Pakistan. The VDS stages 1 to 4 were apparent in 1 a 4 foram aparentes na espécie. A intensidade Thais carinifera. The intensity of imposex has do imposex permaneceu comparativamente baixa remained comparatively low in the populations of nas populações dos portos próximos do porto de harbours in close proximity to port Mohammad Mohammad Bin-Qasim, especificamente em Old Bin-Qasim, namely; Old Korangi Fish Harbour Korangi Fish Harbour (OKFH) e New Korangi Fish (OKFH) and New Korangi Fish Harbour (NKFH) Harbour (NKFH), onde as atividades portuárias where shipping activities are sporadic as compared são esporádicas quando comparadas às de Manora to those in Manora Channel and the adjoining Channel e à área adjacente do Porto de Karachi, onde Karachi Port area where intensive shipping activity a atividade portuária é mais intensa.
    [Show full text]
  • Tributyltin and Its Derivative in Water Samples of National Inland Water
    ry: C ist urr m en e t h Ogbomida and Ezemonye, Organic Chem Curr Res 2016, 5:1 R C e c s i e n a DOI: 10.4172/2161-0401.1000158 a r Organic Chemistry c g r h O ISSN: 2161-0401 Current Research ResearchResearch Article Article OpenOpen Access Access Tributyltin and its Derivative in Water Samples of National Inland Water Way Authority Harbour of Warri, Delta State, Nigeria Ogbomida ET1* and Lawrence Ikechukwu Ezemonye2 1Department of Animal and Environmental Biology, Faculty of Life Science, University of Benin, Nigeria 2Ecotoxicology and Environmental Forensic Unit, National Centre for Energy and Environment, Energy Commission of Nigeria, University of Benin, Nigeria Abstract Surface water samples were collected and analyzed to evaluate the fate of tributyltin (TBT) and its derivatives dibutyltin (DBT) and monobutyltin (MBT) from National Inland Waterway Authority (NIWA) Harbour, using gas chromatography coupled with flame ionization detection (GC-FID) with detection limit of 0.001 µg/l. The concentrations were in the range of TBT (0.01 µg/l to 0.05 µg/l), DBT (0.01 µg/l to 0.03 µg/l) and MBT (0.01 µg/l to 0.02 µg/l). The total butyltin concentration ranged from 0.04 µg/l to 0.09 µg/l. TBT was generally dominant in most of the samples, suggesting fresh inputs of tributyltin compounds and/or less degradation of TBT. The measured mean concentrations in surface water samples exceeded the ecotoxicological benchmark of 0.01 µg/l recommended by US Environmental Protection Agency (USEPA) indicative of potential environmental risk.
    [Show full text]