Determination of Organotin Compounds in Coastal Sediment Pore-Water by Diffusive Gradients in Thin-Films (DGT) Technique

Total Page:16

File Type:pdf, Size:1020Kb

Determination of Organotin Compounds in Coastal Sediment Pore-Water by Diffusive Gradients in Thin-Films (DGT) Technique Determination of organotin compounds in coastal sediment pore-water by diffusive gradients in thin-films (DGT) technique by Russell Francis Cole Submitted in partial fulfilment of a degree of Doctor of Philosophy in the Faculty of Science September 2016 University of Portsmouth School of Earth and Environmental Sciences Burnaby Building Burnaby Road Portsmouth PO1 3QL Abstract Organotin compounds still present a high risk to biota in the aquatic environment. Measuring the behaviour of the freely dissolved fractions of these compounds in sediment compartments is challenging, with costly and sensitive analytical techniques required for their measurement. Diffusive gradients in thin-films (DGT) allow for the uptake and pre-concentration of analytes in a binding gel and is used to measure dissolved metals and some organic compounds. The utility of novel silica-bound sorbents (C8, C18, mixed phases) as DGT binding gels for the sequestration of organotins in the marine environment was the primary focus of work in this project. The C8 sorbent showed the optimum performance in the uptake and recovery of organotins across pH, ionic strength and in filtered sea water. It was used subsequently as the binding layer in DGT sediment devices (160 mm × 34 mm) overlaid with a mixed-cellulose ester membrane (0.45 µm) as the single diffusion layer. These were used to investigate pore water mobilisation and concentrations of organotins in coastal sediment cores collected from a contaminated site. Organotins demonstrated a non-sustained uptake scenario, with DGT flux and freely dissolved concentrations in pore water measured to decline at 1 cm depth intervals over deployments of 2-28 days. Using time series, concentrations in pore water at t = 0 were calculated providing empirical pore water depletion curves for sediment cores. Using standard laboratory instrumentation (i.e. gas chromatography-mass spectrometry) low limits of detection were achieved (TBT = 0.4 ng L-1 after 2 weeks of sampling). ii Contents 1.1. Organotin compounds in the environment .............................................. 1 1.1.1. Chemistry and application of organotin compounds ................... 1 1.1.2. Behaviour, fate and degradation ................................................ 6 1.1.3. Partitioning behaviour ................................................................. 8 1.1.4. Sediment profiling and the mobilisation of organotins to sediment pore waters ............................................................... 11 1.1.5. Degradation of organotin compounds ...................................... 13 1.1.5.1. Butyltin degradation index (BDI) and phenyltin degradation index (PhDI) ............................................................................. 14 1.1.6. Toxicity ..................................................................................... 15 1.2. The analysis of organotin compounds ................................................... 22 1.2.1. Extraction ................................................................................. 22 1.2.1.1. Reagents ........................................................................... 22 1.2.1.2. Techniques ........................................................................ 23 1.2.2. Derivatisation ........................................................................... 31 1.2.3. Separation ................................................................................ 32 1.2.3.1. Gas chromatography ......................................................... 32 1.2.3.2. Liquid chromatography ...................................................... 32 1.2.4. Detection .................................................................................. 33 1.2.5. Quantification ........................................................................... 35 1.3. Monitoring techniques for organotin compounds in water ......... 36 1.3.1. Discrete sampling ..................................................................... 36 1.3.2. Biological monitoring ................................................................ 36 iii 1.3.3. Electrochemical ........................................................................ 38 1.3.4. Passive sampling techniques for monitoring organotin compounds in water ................................................................. 39 1.3.4.1. Chemcatcher® .................................................................... 42 1.3.4.2. Silicone rubber sheets ....................................................... 43 1.3.4.3. SPMDs .............................................................................. 44 1.4. Monitoring techniques for organotin compounds in sediments and in sediment pore-waters ............................................................... 45 1.4.1. Discrete sampling ..................................................................... 45 1.4.2. Passive sampling techniques for monitoring organotin compounds in sediment ........................................................... 46 1.5. Regulation and management of organotin compounds in the aquatic environment ................................................................................................. 48 1.5.1. International regulations and quality guideline standards ......... 48 1.5.2. Management of contaminated dredged sediments within England and Wales .................................................................. 50 1.5.2.1. Sea disposal ...................................................................... 53 1.5.2.2. Inland disposal ................................................................... 55 1.5.2.3. Monitoring by Cefas ........................................................... 57 1.6. Aims and objectives of research project ...................................................... 59 2.1. Introduction ........................................................................................... 61 2.2. Instrument ............................................................................................. 62 2.3. Chemicals and Reagents ...................................................................... 64 2.3.1. Safety Protocols ....................................................................... 64 2.3.2. Standards ................................................................................. 65 2.3.3. Reagents .................................................................................. 66 2.3.3.1. 1% Sodium tetraethyl borate (1 % NaBEt4 (w/v)) ............... 67 2.3.3.2. 1 M Acetate buffer (1 L) ..................................................... 67 2.3.3.3. 13 M methanolic acetic acid (1 L) ...................................... 68 2.3.3.4. 20% (approximate) sodium hydroxide (NaOH) solution ........ (~ 1 L) ............................................................................... 69 2.3.4. Preparation of glassware/FEP centrifuge tubes ....................... 69 2.4. Simultaneous extraction and derivatisation of sea water ...................... 69 iv 2.4.1. Sampling of sea water .............................................................. 69 2.4.2. Sampling of sediment ............................................................... 70 2.4.3. Extraction and derivatisation .................................................... 70 2.5. Extraction and derivatisation of sediment samples ................... 71 2.5.1. Extraction and derivatisation .................................................... 71 2.6. Calibration ................................................................................. 75 2.6.1. Calibration for water analysis ................................................... 75 2.6.2. Calibration for sediment analysis.............................................. 75 2.6.3. Summary of calibration parameters.......................................... 76 2.7. Development of a cold programmed temperature vaporisation-large volume injection (PTV-LVI) technique for organotin compounds ................. 79 2.7.1. Background .............................................................................. 79 2.7.1.1. Inlet and injection parameters ............................................ 80 2.7.1.2. Limits of detection for splitless injection/PTV-LVI .............. 85 2.8. Validation of methods .................................................................................. 87 2.8.1. Organotins in water .................................................................. 87 2.8.2. Organotins in sediment ............................................................ 88 2.8.3. Field samples ........................................................................... 90 2.8.3.1. Sea water........................................................................... 90 2.8.3.2. Further developmental work .............................................. 91 2.8.3.3. Sediment............................................................................ 92 2.9. Summary ...................................................................................................... 92 3.1. Introduction ................................................................................................... 95 3.1.1. Theory ...................................................................................... 95 3.1.2. Considerations for DGT ............................................................ 97 3.1.2.1. pH and ionic strength ......................................................... 97 3.1.2.2. Biofouling ..........................................................................
Recommended publications
  • Aldrich Organometallic, Inorganic, Silanes, Boranes, and Deuterated Compounds
    Aldrich Organometallic, Inorganic, Silanes, Boranes, and Deuterated Compounds Library Listing – 1,523 spectra Subset of Aldrich FT-IR Library related to organometallic, inorganic, boron and deueterium compounds. The Aldrich Material-Specific FT-IR Library collection represents a wide variety of the Aldrich Handbook of Fine Chemicals' most common chemicals divided by similar functional groups. These spectra were assembled from the Aldrich Collections of FT-IR Spectra Editions I or II, and the data has been carefully examined and processed by Thermo Fisher Scientific. Aldrich Organometallic, Inorganic, Silanes, Boranes, and Deuterated Compounds Index Compound Name Index Compound Name 1066 ((R)-(+)-2,2'- 1193 (1,2- BIS(DIPHENYLPHOSPHINO)-1,1'- BIS(DIPHENYLPHOSPHINO)ETHAN BINAPH)(1,5-CYCLOOCTADIENE) E)TUNGSTEN TETRACARBONYL, 1068 ((R)-(+)-2,2'- 97% BIS(DIPHENYLPHOSPHINO)-1,1'- 1062 (1,3- BINAPHTHYL)PALLADIUM(II) CH BIS(DIPHENYLPHOSPHINO)PROPA 1067 ((S)-(-)-2,2'- NE)DICHLORONICKEL(II) BIS(DIPHENYLPHOSPHINO)-1,1'- 598 (1,3-DIOXAN-2- BINAPH)(1,5-CYCLOOCTADIENE) YLETHYNYL)TRIMETHYLSILANE, 1140 (+)-(S)-1-((R)-2- 96% (DIPHENYLPHOSPHINO)FERROCE 1063 (1,4- NYL)ETHYL METHYL ETHER, 98 BIS(DIPHENYLPHOSPHINO)BUTAN 1146 (+)-(S)-N,N-DIMETHYL-1-((R)-1',2- E)(1,5- BIS(DI- CYCLOOCTADIENE)RHODIUM(I) PHENYLPHOSPHINO)FERROCENY TET L)E 951 (1,5-CYCLOOCTADIENE)(2,4- 1142 (+)-(S)-N,N-DIMETHYL-1-((R)-2- PENTANEDIONATO)RHODIUM(I), (DIPHENYLPHOSPHINO)FERROCE 99% NYL)ETHYLAMIN 1033 (1,5- 407 (+)-3',5'-O-(1,1,3,3- CYCLOOCTADIENE)BIS(METHYLD TETRAISOPROPYL-1,3- IPHENYLPHOSPHINE)IRIDIUM(I)
    [Show full text]
  • Alfa Laval Black and Grey List, Rev 14.Pdf 2021-02-17 1678 Kb
    Alfa Laval Group Black and Grey List M-0710-075E (Revision 14) Black and Grey list – Chemical substances which are subject to restrictions First edition date. 2007-10-29 Revision date 2021-02-10 1. Introduction The Alfa Laval Black and Grey List is divided into three different categories: Banned, Restricted and Substances of Concern. It provides information about restrictions on the use of Chemical substances in Alfa Laval Group’s production processes, materials and parts of our products as well as packaging. Unless stated otherwise, the restrictions on a substance in this list affect the use of the substance in pure form, mixtures and purchased articles. - Banned substances are substances which are prohibited1. - Restricted substances are prohibited in certain applications relevant to the Alfa Laval group. A restricted substance may be used if the application is unmistakably outside the scope of the legislation in question. - Substances of Concern are substances of which the use shall be monitored. This includes substances currently being evaluated for regulations applicable to the Banned or Restricted categories, or substances with legal demands for monitoring. Product owners shall be aware of the risks associated with the continued use of a Substance of Concern. 2. Legislation in the Black and Grey List Alfa Laval Group’s Black and Grey list is based on EU legislations and global agreements. The black and grey list does not correspond to national laws. For more information about chemical regulation please visit: • REACH Candidate list, Substances of Very High Concern (SVHC) • REACH Authorisation list, SVHCs subject to authorization • Protocol on persistent organic pollutants (POPs) o Aarhus protocol o Stockholm convention • Euratom • IMO adopted 2015 GUIDELINES FOR THE DEVELOPMENT OF THE INVENTORY OF HAZARDOUS MATERIALS” (MEPC 269 (68)) • The Hong Kong Convention • Conflict minerals: Dodd-Frank Act 1 Prohibited to use, or put on the market, regardless of application.
    [Show full text]
  • Hazardous Substances (Chemicals) Transfer Notice 2006
    16551655 OF THURSDAY, 22 JUNE 2006 WELLINGTON: WEDNESDAY, 28 JUNE 2006 — ISSUE NO. 72 ENVIRONMENTAL RISK MANAGEMENT AUTHORITY HAZARDOUS SUBSTANCES (CHEMICALS) TRANSFER NOTICE 2006 PURSUANT TO THE HAZARDOUS SUBSTANCES AND NEW ORGANISMS ACT 1996 1656 NEW ZEALAND GAZETTE, No. 72 28 JUNE 2006 Hazardous Substances and New Organisms Act 1996 Hazardous Substances (Chemicals) Transfer Notice 2006 Pursuant to section 160A of the Hazardous Substances and New Organisms Act 1996 (in this notice referred to as the Act), the Environmental Risk Management Authority gives the following notice. Contents 1 Title 2 Commencement 3 Interpretation 4 Deemed assessment and approval 5 Deemed hazard classification 6 Application of controls and changes to controls 7 Other obligations and restrictions 8 Exposure limits Schedule 1 List of substances to be transferred Schedule 2 Changes to controls Schedule 3 New controls Schedule 4 Transitional controls ______________________________ 1 Title This notice is the Hazardous Substances (Chemicals) Transfer Notice 2006. 2 Commencement This notice comes into force on 1 July 2006. 3 Interpretation In this notice, unless the context otherwise requires,— (a) words and phrases have the meanings given to them in the Act and in regulations made under the Act; and (b) the following words and phrases have the following meanings: 28 JUNE 2006 NEW ZEALAND GAZETTE, No. 72 1657 manufacture has the meaning given to it in the Act, and for the avoidance of doubt includes formulation of other hazardous substances pesticide includes but
    [Show full text]
  • Toxicological Profile for Tin and Tin Compounds
    TIN AND TIN COMPOUNDS 23 3. HEALTH EFFECTS 3.1 INTRODUCTION The primary purpose of this chapter is to provide public health officials, physicians, toxicologists, and other interested individuals and groups with an overall perspective on the toxicology of ton and tin compounds. It contains descriptions and evaluations of toxicological studies and epidemiological investigations and provides conclusions, where possible, on the relevance of toxicity and toxicokinetic data to public health. A glossary and list of acronyms, abbreviations, and symbols can be found at the end of this profile. Because there is such a large number of inorganic tin and organotin compounds, only the most widely studied compounds and those that present the greatest potential for human exposure have been selected for the discussion of health effects. In addition to primary studies, review articles and government reports are occasionally provided in order to assist the reader in understanding more fully the toxicology of the tin compounds. 3.2 DISCUSSION OF HEALTH EFFECTS BY ROUTE OF EXPOSURE To help public health professionals and others address the needs of persons living or working near hazardous waste sites, the information in this section is organized first by route of exposure (inhalation, oral, and dermal) and then by health effect (death, systemic, immunological, neurological, reproductive, developmental, genotoxic, and carcinogenic effects). These data are discussed in terms of three exposure periods: acute (14 days or less), intermediate (15–364 days), and chronic (365 days or more). Levels of significant exposure for each route and duration are presented in tables and illustrated in figures. The points in the figures showing no-observed-adverse-effect levels (NOAELs) or lowest- observed-adverse-effect levels (LOAELs) reflect the actual doses (levels of exposure) used in the studies.
    [Show full text]
  • Environmental Health Criteria 15 TIN and ORGANOTIN COMPOUNDS A
    Environmental Health Criteria 15 TIN AND ORGANOTIN COMPOUNDS A Preliminary Review Please note that the layout and pagination of this web version are not identical with the printed version. Tin and organotin compounds (EHC 15, 1980) INTERNATIONAL PROGRAMME ON CHEMICAL SAFETY ENVIRONMENTAL HEALTH CRITERIA 15 TIN AND ORGANOTIN COMPOUNDS A Preliminary Review This report contains the collective views of an international group of experts and does not necessarily represent the decisions or the stated policy of either the World Health Organization or the United Nations Environment Programme. Published under the joint sponsorship of the United Nations Environment Programme and the World Health Organization World Health Organization Geneva, 1980 ISBN 92 4 154075 3 (c) World Health Organization 1980 Publications of the World Health Organization enjoy copyright protection in accordance with the provisions of Protocol 2 of the Universal Copyright Convention. For rights of reproduction or translation of WHO publications, in part or in toto, application should be made to the Office of Publications, World Health Organization, Geneva, Switzerland. The World Health Organization welcomes such applications. The designations employed and the presentation of the material in this publication do not imply the expression of any opinion whatsoever on the part of the Secretariat of the World Health Organization concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries. The mention of specific companies or of certain manufacturers' products does not imply that they are endorsed or recommended by the World Health Organization in preference to others of a similar nature that are not mentioned.
    [Show full text]
  • Biological Activity of Organotin Compounds--An Overview
    ENVIRONMENTAL RESEARCH 44, 335-353 (1987) Biological Activity of Organotin Compounds--An Overview N. J. SNOEIJ, A. H. PENNINKS, AND W. SEINEN Department of Veterinary Pharmacology, Pharmacy, and Toxicology, University of Utrecht, Biltstraat 172, Building A9, 3572 BP, Utrecht, The Netherlands Received November 21, 1986 As a consequence of the rapid expansion of the uses and applications of the organotin compounds, the concern about their environmental and health effects is increasing. The main subject of this overview is the current understanding of the mammalian toxicity of the organotin compounds. Four different types of target organ toxicity, namely neurotoxicity, hepatotoxicity, immunotoxicity, and cutaneous toxicity, are discussed in more detail. The effects of the organotin compounds on the mitochondfial and cellular level are summarized and discussed in relation to the mode of action of these compounds on the central nervous system, the liver and bile duct, the immune system, and the skin. © 1987Academic Press, Inc. ORGANOTIN COMPOUNDS: APPLICATIONS AND TOXICITY Organotin Compounds Tin can be present as an element in a wide variety of both inorganic and or- ganometallic compounds. Organometallic tin compounds or organotins are char- acterized by the presence of at least one covalent carbon-tin bond. Although tin may exist either in the Sn 2+ or in the Sn 4+ oxidation state, almost all organotins have a tetravalent structure. Depending on the number of organic moieties, the organotin compounds are classified as mono-, di-, tri-, and tetraorganotins. In compounds of industrial importance, methyl, butyl, octyl, and phenyl groups form the organic substituents, while the anion is usually chloride, fluoride, oxide, hydroxide, carboxylate, or thiolate.
    [Show full text]
  • A Sheffield Hallam University Thesis
    The chemistry of some heteroaryltin compounds. DERBYSHIRE, Diana Jane. Available from the Sheffield Hallam University Research Archive (SHURA) at: http://shura.shu.ac.uk/19555/ A Sheffield Hallam University thesis This thesis is protected by copyright which belongs to the author. The content must not be changed in any way or sold commercially in any format or medium without the formal permission of the author. When referring to this work, full bibliographic details including the author, title, awarding institution and date of the thesis must be given. Please visit http://shura.shu.ac.uk/19555/ and http://shura.shu.ac.uk/information.html for further details about copyright and re-use permissions. I P G I A III Sheffield City Polytechnic Library REFERENCE ONLY I ProQuest Number: 10694436 All rights reserved INFORMATION TO ALL USERS The quality of this reproduction is dependent upon the quality of the copy submitted. In the unlikely event that the author did not send a com plete manuscript and there are missing pages, these will be noted. Also, if material had to be removed, a note will indicate the deletion. uest ProQuest 10694436 Published by ProQuest LLC(2017). Copyright of the Dissertation is held by the Author. All rights reserved. This work is protected against unauthorized copying under Title 17, United States C ode Microform Edition © ProQuest LLC. ProQuest LLC. 789 East Eisenhower Parkway P.O. Box 1346 Ann Arbor, Ml 48106- 1346 THE CHEMISTRY OF SOME HETEROARYLTIN COMPOUNDS by DIANA JANE DERBYSHIRE A Thesis submitted to the Council
    [Show full text]
  • Toxicological Profile for Tin and Tin Compounds
    TOXICOLOGICAL PROFILE FOR TIN AND TIN COMPOUNDS U.S. DEPARTMENT OF HEALTH AND HUMAN SERVICES Public Health Service Agency for Toxic Substances and Disease Registry August 2005 TIN AND TIN COMPOUNDS ii DISCLAIMER The use of company or product name(s) is for identification only and does not imply endorsement by the Agency for Toxic Substances and Disease Registry. TIN AND TIN COMPOUNDS iii UPDATE STATEMENT A Toxicological Profile for Tin and Tin Compounds, Draft for Public Comment was released in September 2003. This edition supersedes any previously released draft or final profile. Toxicological profiles are revised and republished as necessary. For information regarding the update status of previously released profiles, contact ATSDR at: Agency for Toxic Substances and Disease Registry Division of Toxicology/Toxicology Information Branch 1600 Clifton Road NE Mailstop F-32 Atlanta, Georgia 30333 TIN AND TIN COMPOUNDS vi *Legislative Background The toxicological profiles are developed in response to the Superfund Amendments and Reauthorization Act (SARA) of 1986 (Public law 99-499) which amended the Comprehensive Environmental Response, Compensation, and Liability Act of 1980 (CERCLA or Superfund). This public law directed ATSDR to prepare toxicological profiles for hazardous substances most commonly found at facilities on the CERCLA National Priorities List and that pose the most significant potential threat to human health, as determined by ATSDR and the EPA. The availability of the revised priority list of 275 hazardous substances was announced in the Federal Register on November 17, 1997 (62 FR 61332). For prior versions of the list of substances, see Federal Register notices dated April 29, 1996 (61 FR 18744); April 17, 1987 (52 FR 12866); October 20, 1988 (53 FR 41280); October 26, 1989 (54 FR 43619); October 17, 1990 (55 FR 42067); October 17, 1991 (56 FR 52166); October 28, 1992 (57 FR 48801); and February 28, 1994 (59 FR 9486).
    [Show full text]
  • Tin Hazards to Fish, Wildlife, and Invertebrates: a Synoptic Review
    BIOLOGICAL REPORT 85(1.15) Contaminant Hazard Reviews JANUARY 1989 REPORT NO. 15 TIN HAZARDS TO FISH, WILDLIFE, AND INVERTEBRATES: A SYNOPTIC REVIEW by Ronald Eisler U.S. Fish and Wildlife Service Patuxent Wildlife Research Center Laurel, MD 20708 SUMMARY Tin (Sn) has influenced our life style for the past 5,000 years. Today we are exposed to tin on a daily basis; including tinplated baby food cans; alloys such as pewter, bronze, brass, and solder; and toothpaste containing stannous flouride. These inorganic tin compounds are not highly toxic due to their low solubility, poor absorption, low accumulation, and rapid excretion. Synthetic organotin compounds, however, first manufactured commercially in the 1960's, may present a variety of problems to animals, including impaired behavior and reduced growth, survival, and reproduction. Some triorganotins--for example, in antifouling marine paints, in molluscicides, and in agricultural pesticides--can be harmful to sensitive species of nontarget biota at recommended application protocols. Background concentrations of organotin compounds are frequently elevated--occasionally to dangerous levels--in aquatic organisms collected near marinas and other locales where organotin-based antifouling paints are extensively used. But more information is needed on background concentrations of organotins, especially those from terrestrial ecosystems. Tributyltin compounds are especially toxic to aquatic organisms. Adverse effects were noted at concentrations of 0.001 to 0.06 ug/l on molluscs and at 0.1 to 1.0 ug/l on algae, fish, and crustaceans. In general, bioconcentration of organotins from seawater was high, especially by algae, but degradation was sufficiently rapid to preclude food chain biomagnification.
    [Show full text]
  • Hazardous Chemicals Handbook
    Hazardous Chemicals Handbook Hazardous Chemicals Handbook Second edition Phillip Carson PhD MSc AMCT CChem FRSC FIOSH Head of Science Support Services, Unilever Research Laboratory, Port Sunlight, UK Clive Mumford BSc PhD DSc CEng MIChemE Consultant Chemical Engineer Oxford Amsterdam Boston London New York Paris San Diego San Francisco Singapore Sydney Tokyo Butterworth-Heinemann An imprint of Elsevier Science Linacre House, Jordan Hill, Oxford OX2 8DP 225 Wildwood Avenue, Woburn, MA 01801-2041 First published 1994 Second edition 2002 Copyright © 1994, 2002, Phillip Carson, Clive Mumford. All rights reserved The right of Phillip Carson and Clive Mumford to be identified as the authors of this work has been asserted in accordance with the Copyright, Designs and Patents Act 1988 No part of this publication may be reproduced in any material form (including photocopying or storing in any medium by electronic means and whether or not transiently or incidentally to some other use of this publication) without the written permission of the copyright holder except in accordance with the provisions of the Copyright, Designs and Patents Act 1988 or under the terms of a licence issued by the Copyright Licensing Agency Ltd, 90 Tottenham Court Road, London, England W1T 4LP. Applications for the copyright holder’s written permission to reproduce any part of this publication should be addressed to the publishers British Library Cataloguing in Publication Data A catalogue record for this book is available from the British Library Library of Congress Cataloguing
    [Show full text]
  • Organotin Compounds:- Their Analyses and Effect On
    ORGANOTIN COMPOUNDS:- THEIR ANALYSES AND EFFECT ON MODEL BIOMEMBRANES BY BASIL UGWUNNA NWATA B.Sc (Hons), University of Ilorin, Nigeria, 1981 M.Sc, University of Ibadan, Nigeria 1984 M.Sc, University of British Columbia, Canada 1989 A THESIS SUBMITrID IN PARTIAL FULFILLMENT OF THE REQUIREMENTS FOR THE DEGREE OF DOCTOR OF PHILOSOPHY IN THE FACULTY OF GRADUATE STUDIES DEPARTMENT OF CHEMISTRY We accept this thesis as conforming to the required standard COLUMBIA JUNE 1994 © Basil Ugwunna Nwata, 1994 __________________ In presenting this thesis in partial fulfilment of the requirements for an advanced degree at the University of British Columbia, I agree that the Library shall make it freely available for reference and study. I further agree that permission for extensive copying of this thesis for scholarly purposes may be granted by the head of my department or by his or her representatives. It is understood that copying or publication of this thesis for financial gain shall not be allowed without my written permission. (Signature) Department of C/17’1’ i7’ The University of British Columbia Vancouver, Canada Date ditW4 i’? DE-6 (2)88) 11 ABSTRACT Studies involving the analyses of organotin compounds in marine organisms of British Columbia, and the effect of organotin compounds on the permeability of model biological membranes are presented in this thesis. Analysis of organotin compounds by gas chromatography-selected ion monitoring mass spectrometry (GC-MS SIM) affords a very specific technique for the identification and quantitation of organotin compounds, by using the peculiar isotope pattern for tin compounds. This methodology is therefore able to distinguish organotin compounds from other compounds that may co-elute with them from the gas chromatograph.
    [Show full text]