|
1. |
Back matter |
|
Journal of Analytical Atomic Spectrometry,
Volume 10,
Issue 11,
1995,
Page 024-025
Preview
|
PDF (216KB)
|
|
摘要:
1996 Winter Conference on Plasma Spectrochemistry Fort Lauderdale Florida January 8 - 73 7996 The 1996 Winter Conference on Plasma Spectrochemistry ninth in a series of biennial meetings sponsored by the /CP information Newsletter features developments in plasma spectrochemical analysis by inductively coupled plasma (ICP) dc plasma (DCP) microwave plasma (MIP) and glow discharge (GDL HCL) sources. The meeting will be held Monday January 8 through Saturday January 13 1996 at the Bonaventure World Conference Center in Fort Lauderdale Florida. Continuing education short courses at introductory and advanced levels will be offered Friday through Sunday January 5 - 7. Spectroscopic instrumentation and accessories will be shown during a three-day exhibition. Objectives and Program The continued growth in popularity of plasma sources for atomization and excitation in atomic spectroscopy and ionization in mass spectrometry and the need to discuss recent developments of these discharges in spectrochemical analysis stimulated the organization of this meeting.The Conference will bring together international scientists experienced in applications instrumentation and theory in an informal setting to examine recent progress in the field. Approximately 500 participants from 25 countries are expected to attend. Approximately 300 papers describing applications fundamentals and instrumental developments with plasma sources are expected to be presented in lecture and poster sessions by more than 200 authors. Symposia organized and chaired by recognized experts will include the following topics 1) Sample introduction and transport phenomena 2) Flow injection spectrochemical analysis 3) Elemental speciation with plasma/chromatographic techniques 4) Plasma instrumentation including chemometrics expert systems on-line analysis software and remote-system automation 5) Sample preparation treatment and automation 6) Excitation mechanisms and plasma phenomena 7) Spectroscopic standards and reference materials 8) Plasma source mass spectrometry 9) Glow discharge atomic and mass spectrometry 10) Applications of stable isotope analyses and 1 1) Laser-assisted plasma spectrometry. Six plenary and 18 invited lectures will highlight advances in these areas. Afternoon poster sessions will feature applications automation and new instrumentation. Five panel discussions will address critical development areas in sample introduction instrumentation elemental speciation plasma source mass spectrometry and novel software and hardware directions.Plenary invited and submitted papers will be published in Fall 1996 after peer review as the official Conference proceedings. Schedule of Activities Preliminary Title and 50-Word Abstract Due for Contributed Papers Exhibitor Booth Reservation and Pre-Registration Deadline Conference Pre-Registration October 13,1995 Hotel Pre-Reservation October 13 1995 Late Pre-Registration Deadline December 8,1995 1996 Winter Conference Short Courses January 5 - 7,1996 1 996 Winter Conference on Plasma Spectrochemistty January 8 - 13,1996 July 3 1995 September 11 1995 Further Information For further information return this form to 1996 Winter Conference on Plasma Spectrochemistry %lCP information Newsletter Department of Chemistry Lederle GRC Towers University of Massachusetts Box 34510 Amherrt MA 01003-4510 USA.ATTN Or. Ramon Barnes Conference Chairman Telephone (41 3) 545-2294 Telefax (41 3) 545-4490. % 0 Send further information. 0 I plan to attend accompanied by 0 I plan to present a paper (D oral 0 poster 0 computer poster). Title 1996 WlNTER CONFERENCE ON PLASMA SPECTROCHEMlSTRY Name Organization Address city Telephone Title State/Country Telefax Date ZIP/Postal Code EMAlLRoyal Society of Chemistry Analytical Division Atomic Spectroscopy Group Eighth Biennial National Atomic Spectroscopy Symposium 8th BNASS University of East Anglia UK 17-20 July 1996 Plenary Lectulers Invited Lecturers call for Papers social Programm workshop Further Detaila Dr S J Hill Professor N Furuta.Professor F Adams Professor J M M e m t and Professor G Hieftje Dr 0 Donard Dr S J Pmy. Dr S Fairweather-Tait Dr A Ellis Dr A G Howard. Dr J Brtnner. Dr J Mmhdl Dr N J Miller-lhli Dr S Tanner and Professor D Littlejohn Contributed oral and poster presentations on recent developments in both p u n and applied atomic spectroscopy - analytical applications theoretical studies or fundamental advances in AAS A m . AFS. inorganic MS and XRF. Thm copies of abstracts must be submitted before 2% February 1996. BNASS has an enviable reputation of being a friendly and dynamic meeting. A number of social events including a Symposium Dinner will form an integral part of the meeting.Immediately prior to the 8th BNASS then will be a Short Course on Sample Pre-treatment and Sample Introduction for Atomic Spectroscopy. 17 July a.m. 1996. Ms Brenda Holliday. Royal Society of Chemistry Thomas Graham House. Science Park Milton Road Cluabridgc Cl34 4WF. UK. T e l M (0)1223 420066; Fax +44 (0)1223 420247; E - d l JAAS@RSC.ORG 1996 WINTER CONFERENCE ON PLASMA SPECTROCHEMISTRY January 843,1996 at the Bonaventure World Conference Center Fort Lauderdale Florida USA Short Course on High-resolution ICP-/US (Sl-3) It is the aim of a short course at the 1996 Winter Conference on Plasma Spectrochemistry (January Sth 7pm) to summarize the state of the art in HR-ICP-MS. The course provides an introduction to ICP-MS with a double focusing magnetic sector mass analyser.This course uffers fundamental background a thorough discussion of analytical features and state of the art information on applications. Different types of double focusing instruments also are considered. Specific topics include fundamental aspects of ICP-MS (physical properties of a double focusing instrument operational characteristics in comparison with quadrupole instruments); analytical characteristics (spectral and non-spectral interferences figures of merit in low and high resolution modes blanks and memory effects HPLC and GC interfaces) and applications (industrial including ultra-pure reagents and alloys environmental geological and biomedical). Course organizers Luc Moens Ghent University Laboratory of Analytical Chemistry Proeftuinstraat 86 8-9000 Ghent Belgium; and Norbert Jakubowski lnstitut fur Spektrochemie und Angewandte Spektroskopie Bunsen Kirchoff-Strasse 11 0-44139 Dortmund Germany. For registration and further information on the Conference and short course please contact Dr. Ramon Barne8 Conference Chairman Department of Chemistry Lederle GRC Tower University of Massachusetts Box 3451 0 Amherst MA 01 003-451 0. Tol 41 3 545 2294; Fax 41 3 545 3757
ISSN:0267-9477
DOI:10.1039/JA99510BP024
出版商:RSC
年代:1995
数据来源: RSC
|
2. |
Diary of conferences and courses |
|
Journal of Analytical Atomic Spectrometry,
Volume 10,
Issue 11,
1995,
Page 59-61
Preview
|
PDF (271KB)
|
|
摘要:
Journal of Analytical Atomic Spectrometry DIARY OF CONFERENCES AND COURSES 1995 Street Sheffield S1 4CT UK. Fax +44 (0) 114 2768653. developments in the near infrared (NIR) and Raman techniques. The latter has been characterized by new instruments that strongly reduce the Short Course Disposal of Hazardous Waste December 5 Scheele Symposium 1995 on earlier problem with interfering This workshop will focus on Shefield UK Details can be found in J. Anal. At. Spectrom. 1995 10 34N. For further information contact Ms Baldham or Ms Rogers Division of Adult Continuing Education University of Sheffield 196-198 West a renaissance with particular given. ('1 '14 2825391; Modern Applications of Vibrational fluoresence. Spectrometry December 8 Uppsala Sweden Vibrational spectrometry is undergoing pharmaceutical applications on the three techniques FT-IR Raman and NIR.Lectures by the Scheele awardee 1995 professor Patrick Hendra and other experienced spectrometrists as well as graduate students will be Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 59NFor further information contact Christel Anderson The Swedish Academy of Pharmaceutical Sciences P.O. Box 1136 11181 Stockholm Sweden. Telephone +46 8 723 5000. Fax +46 8 20 5511. International Symposium on Environmental Biomonitoring and Specimen Banking December 17-22 Honolulu Hawaii USA Details can be found in J. Anal. At. Spectrom. 1994 9 59N. For further information contact K. S. Subramanian Environmental Health Directorate Health Canada Tunney's Pasture Ottawa Ontario K1A OL2 Canada (phone 613-957-1874; fax 613-941-4545) or G.V. Iyengar Center for Analytical Chemistry Room 235 B 125 National Institute of Standards and Technology Gaithersburg MD 20899 USA (Telephone +1 301 975 6284; Fax + 1 301 921 9847) or M. Morita Division of Chemistry and Physics National Institute for Environmental Studies Japan Environmental Agency Yatabe-Machi Tsukuba Ibaraki 305 Japan (Telephone +81 298 51 6111 ext. 260; Fax +81 298 56 4678). 1996 1996 Winter Conference on Plasma Spectrochemistry January 8-13 Fort Lauderdale Florida USA Details can be found in J. Anal. At. Spectrom. 1994,9,53N. For further information contact Dr. R. Barnes ICP Information Newsletter Department of Chemistry Lederle GRC Towers University of Massachusetts Box 34510 Amherst MA 01003-4510 USA.Telephone + 1 413 545 2294; Telefax + 1 413 545 4490. International Schools and Conferences on X-Ray Analytical Methods January 18-25 Sydney Australia Details can be found in J. Anal. At. Spectrom. 1994,9,47N. For further information contact AXAA '96 Secretariat GPO Box 128 Sydney NSW 2001 Australia. Telephone + 61 2 262 2277; Fax + 61 2 262 2323; Telex AA 17651 1 TRHOST. 8th Sanibel Conference on Mass Spectrometry Metal-Containing Ions and Their Applications in Mass Spectrometry January 20-23 Sanibel Island FL USA For further details contact American Society for Mass Spectrometry 1201 Don Diego Avenue Santa Fe NM 87505 USA. Telephone + 1 505 989 4517; Fax + 1 505 989 1073. Analytica Conference 96 April 23-26 Munich Germany Details can be found in J.Anal. At. Spectrom. 1994,2,69N. For further information contact Messe Miinchen GmbH Messegelande D-80325 Miinchen Germany. Telephone +49 89 51 07 0; Telex 5 212 086 ameg d; Fax +49 89 51 07 177. ASMS Short Course Interpretation of Mass Spectra LC/MS and MS/MS May 11-12 Portland OR USA For further details contact American Society of Mass Spectrometry 1201 Don Diego Avenue Santa Fe NM 87505 USA. Telephone + 1 505 989 4517; Fax + 1 505 989 1073. 44th ASMS Conference on Mass Spectrometry and Allied Topics May 12-17 Portland OR USA For further details contact American Society of Mass Spectrometry 1201 Don Diego Avenue Santa Fe NM 87505 USA. Telephone + 1 505 989 4517; Fax + 1 505 989 1073. Ninth International Symposium on Trace Elements in Man and Animals May 19-24 Ban# Alberta Canada Details can be found in J.Anal. At. Spectrom. 1995,10 58N. For further details contact TEMA-9 The Banff Centre for Conferences P.O. Box 1020 Station 11 Banff Alberta Canada TOL OCO. Telephone + 1 403 762 6308; Fax + 1 403 762 6388 or Dr. Mary L'AbbC. Telephone + 1 613 957 0924; Fax + 1 613 941 6182; EM AIL Mlabbe@HPB.HWC.CA. Total Reflection X-Ray Fluorescence Analysis 10-11 June 1996 Eindhoven Germany 13-14 June 1996 Dortmund Germany The conference will present the state-of- the-art in instrumental and methodological development and demonstrate actual applications. Besides conventional total reflection X-ray fluorescence analysis related methods like X-Ray reflectometry and grazing- emission XRF will be included. The first two days in Eindhoven will focus on surface and thin layer analysis the last two days in Dortmund on micro- and trace analysis.Like the preceeding conferences in Geesthacht (1986 and 1992) Dortmund (1988) Vienna (1990) and Tsukuba (1994) the 6th conference will bring together scientists users instrument manufacturers and all who are interested in the chosen subject. Apart from a few invited lectures contributed papers and posters will constitute the scientific programme. Substantial discussions and exchange of experience are encouraged. For further details contact Gesellschaft Deutscher Chemiker TXRF-Konferenz Postfach 90 04 40 D-60444 Frankfurt Germany. Fax + 49 69 7917 475. Resonance Ionization Spectroscopy June 30-July 5 1996 Pennsylvania USA The Eighth International Symposium on Resonance Ionization Spectroscopy and Its Applications (RIS-96) is an ongoing series of meetings which began in 1980 in Knoxville Tennessee.The conference program will focus on progress in understanding fundamental processes on developments in instrumentation and on new analytical applications. Related disciplines where RIS may play a role in the future will also be featured. The scientific program will consist of keynote and invited lectures as well as contributed oral and poster present a tions. For more information contact Sabrina Glasgow Conference Secretary Department of Chemistry The Pennsylvania State University 184 Materials Research Institute Building University Park PA 16802- 7003 USA. Tel + 1 814 865 0200; Fax +18148630618; Email scg4@psuvm.psu.edu Eighth Biennial National Atomic Spectroscopy Symposium July 17-19 University of East Anglia Norwich UK The Biennial National Atomic Spectroscopy Symposium has an international reputation as the United Kingdom's premier meeting in the field of analytical atomic spectroscopy. The aim of this three day meeting is to 60 N Journal of Analytical Atomic Spectrometry November 1995 Vol.10promote and encourage developments in both fundamental and applied atomic spectroscopy including ICP-MS and XRF by providing a friendly environment where delegates can meet formally and informally to exchange ideas views and results. Plenary lectures given by world renowned spectroscopists provide overviews of important areas of atomic spectroscopy. Invited and submitted lectures as well as posters cover the most recent developments in both pure and applied atomic spetcroscopy.Although the majority of papers tend to focus on analytical applications presentations on theoretical studies or fundamental advances in AA AE AF and XRF are also important components of each BNASS. Preparation and Sample Introduction has been organised for the morning of Wednesday July 27. The course will include aspects of ICP-AES AAS AES XRF AFS and ICP-MS. Separate registration is required. Papers should discuss original unpublished work. Manuscripts of accepted papers will be considered for publication in a special issue JAAS. A Short Course of Sample For further information contact Dr. S. J. Haswell School of Chemistry University of Hull Hull HU6 7RX UK.Telephone + 44 (0)482 465469; Fax + 44 (0)482 466410. 12th Asilomar Conference on Mass Spectrometry Elemental Mass Spectrometry September 20-24 PaciJic Grove CA USA For further details contact American Society of Mass Spectrometry 1201 Don Diego Avenue Santa Fe NM 87505 USA. Telephone + 1 505 989 4517; Fax + 1 505 989 1073. 1997 Seventh International Symposium on Biological and Environmental Reference Materials April 21-25 Antwerp Belgium Details can be found in J. Anal. At. Spectrom. 1995,9,54N. For further details contact Dr J. Pauwels Institute for Reference Materials & Measurements Management of Reference Materials Unit Retieseweg B-2440 Geel Belgium. Telephone + 32 14 571 722; Fax + 32 14 590 406; or Wayne R. Wolf Ph.D Food Composition Laboratory USDA 10300 Baltimore Blvd. Beltsville MD 20705 USA. Telephone + 1 301 504 8927; Fax + 1 301 504 8314 XXX Colloquium Spectroscopicum Internationale September 21st -26t h Melbourne Australia Details can be found in J. Anal. At. Spectrom. 1995,10,58N. For further details contact The Meeting Planners 108 Church Street Hawthorn Victoria 3 122 Australia. Telephone +613 9819 3700; Fax +61 3 9819 5978. Updated information may be obtained from the XXX CSI homepage on the World Wide Web at http://www.latrobe.edu.au/CSIconf/ XXXCSI. html. Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 61 N
ISSN:0267-9477
DOI:10.1039/JA99510059Nb
出版商:RSC
年代:1995
数据来源: RSC
|
3. |
Front cover |
|
Journal of Analytical Atomic Spectrometry,
Volume 10,
Issue 11,
1995,
Page 061-062
Preview
|
PDF (1392KB)
|
|
摘要:
Journal of Analytical Atomic Spectrometry JAAS Editorial Board Chairman. B. L. Sharp (Loughborough UK) A. T. Ellis (Abingdon. UK) R. C. Hutton (Cheshire UK) B. P. Holliday (Cambridge UK) D. Littlejohn (Glasgow UK) S. J. Haswell (Hull UK) H. Crews (Norwich UK) S. J. Hill (Plymouth UK) A. Sanz-Medel (Ovredo Spain) P. D. P. Taylor (Gee/ Belgrum) ~~ ~ JAAS Advisory Board F. C. Adanis (Antwerp Belgrum) G. M. Hieftje (Bloomington IN USA) R. M. Barnes (Amherst MA USA) R. S. Houk (Ames /A. USA) L. Bezur (Budapest Hungary) R. Klockenkamper (Dortmund Germany) M. W. Blades (Vancouver Canada) 6. V. L'vov (St. Petersburg Russia) R. F. Browner (Atlanta GA USA) R. K. Marcus (Clemson SC USA) J L. Burguera (Merida. Venezuela) J. M. Mermet (Vrlleurbanne France) S. Caroli (Rome. Italy) T. Nakahara (Osaka Japan) J.A. Caruso (Crncrnnati OH. USA) Ni Zhe-ming (Beyng China) H. M. Crews (Norwich U K ) J. W. Olesik (Columbus OH USA) A. J. Curtius (Florranopolrs. Brazil) N. Omenetto (lspra Italy) J B. Dawson (Leeds. U K ) C. J. Park (Taelon Korea) M. T. C. de Loos-Vollebregt (Delft The Netherlands) P. J. Potts (Milton Keynes UK) 0. F. X. Donard (Talence France) R. E. Sturgeon (Ottawa Canada) L. Ebdon (Plymouth UK) V. Sychra (Prague Czech Republic) M. S. Epstein (Garthersburg MD USA) P. Van Espen (Antwerp Belgium) Fang Zhao-lun (Shenyang Chrna) R. Van Grieken (Antwerp Belgium) W. Frech (UmeA Sweden) 6. Welz (Uberlrngen. Germany) A. K. Gilmutdinov (Uberlingen Germany) ~~~~ ~~ ~ __ Atomic Spectrometry Updates Editorial Board Chairman *A. T. Ellis (Abingdon UK) J. A.Arnistrong (Edinburgh. UKi 'J. R. Bacon (Aberdeen. UK) R. M. Barnes (Amherst. MA. USA) S . Branch (High Wycombe. U K ) R. Bye (Oslo Norway) J. Carroll (Middlesbrough. UK) M. R. Cave (Keyworth. UK) S. R. N. Chenery (Keyworth. UK) *J. M. Cook (Keyworth. UK) *M. S . Cresser (Aberdeen. UK) H. M. Crews (Norwich. UK) J. S. Crighton (Sunbury-on-Thames U K ) 'J. B. Dawson (Leeds. U K ) J. R. Dean (Newcastle upon Tyne. U K ) *E. H. Evans (Plymouth. UK) J. Fazakas (Budapest Hungary) A. Fisher (Plymouth. UK) L. M. Garden (Middlesbrough. UK) *J. M. Gordon (Cambridge. UK) D. J. Halls (Glasgow UK) K. W. Jackson (Albany. NY USA) R. Jowitt (Middlesbrough. U K ) K. Kitagawa (Nagoya. Japan) J. Kubova (Bratislava Slovak Republrc) *J. Marshall (Mrddlesbrough. UK) * S . J.Hill (P/yf??OutlJ. UK) H. Matusiewicz (Poznan. Poland) A. W. McMahon (Manchester UK) J. M. Mermet (Villeurbanne. France) R. G. Michel (Storrs. CT. USA) *D. L. Miles (Keyworth UK) T. Nakahara (Osaka. Japan) Ni Zhe-ming (Beijing C h m ) P. J. Potts (Milton Keynes UK) W. J. Price (Budlelgh Salterton. U K ) C. J. Rademeyer (Pretoria South Africa) A. Sanz-Medel (Oviedo Spain) *B. L. Sharp (Loughborough UK) I. L. Shuttler (Uberlingen. Germany) S. T. Sparkes (Taunton UK) R. Stephens (Halifax. Canada) J. Stupar (Ljubljana. Slovenia) R. E. Sturgeon (Ottawa. Canada) *A. Taylor (Guildford. UK) G. C. Turk (Gaithersburg MD USA) J. F. Tyson (Amherst. MA USA) P. J. Watkins (London. UK) - B. Welz (Uberlingen Germany) M. White (lspra Italy) J. G. Williams (Egham UK) J. B. Willis (Victoria.Australia) *Members of the ASU Executive Committee ~~ - ._ Managing Editor JAAS Brenda Holliday US Associate Editor JAAS The Royal Society of Chemistry Thomas Graham House Science Park Milton Road Cambridge CB4 4WF UK. Telephone i 44 (0) 1223 420066. Fax t 44 (0) 1223 420247. E-mail RSC1 @RSC.ORG (Internet) Production Manager Janice Gordon Publrshrng Staff Sarah Williams Productron Editorral Staff Yasmin Khan Caroline Seeley Ziva Whitelock Roger Young Editorial Secretaries Lesley Turney Fax 81 -3-381 7-1 895. Claire Harris Frances Thomson Advertisements. Advertisement Department The Royal Society of Chemistry Burlington House Piccadilly London W1V OBN UK. Telephone + 44 (0) 171 -287 3091. Fax + 44 (0) 171 -494 11 34. Dr. J. M. Harnly US Department of Agriculture Beltsville Human Nutrition Research Center Beltsville MI? 20705 USA.Telephone + 1 301 -504-8569 Asia-Pacific Associate Editor JAAS Prof. N. Furuta Department of Applied chemistry Faculty of Science and Engineering Chuo University 1-1 3-27 Kasuga Bunkyo-ku Tokyo 11 2 Japan. Telephone 81 -3-381 7-1 906. E-mail nfuruta(aapchem.chem.chuo-u.ac.jp ~~ ~- __ _~ __ __ Information for Authors Full details of how to submit materials for publi- cation in JAAS are given in the Instructions to Authors in Issue 1. Separate copies are available on request. The Journal of Analytical Atomic Spectrometry (JAAS) is an international journal for the publi- cation of original research papers communi- cations and letters concerned with the development and analytical application of atomic spectrometric techniques. The journal is pub- lished twelve times a year including comprehen- sive reviews of specific topics of interest to practising atomic spectroscopists and incorpor- ates the literature reviews which were previously published in Annual Reports on Analytical Atomic Spectroscopy (ARAAS).Manuscripts intended for publication must describe original work related to atomic spectro- metric analysis. Papers on all aspects of the sub- ject will be accepted including fundamental studies novel instrument developments and prac- tical analytical applications. As well as AAS AES and AFS papers will be welcomed on atomic mass spectrometry X-ray fluorescence/emission spectrometry and secondary emission spec- trometry. Papers describing the measurement of molecular species where these relate to the characterization of sources normally used for the production of atoms or are concerned for example with indirect methods of analysis will also be acceptable for publication.Papers describing the development and applications of hybrid techniques (e.g.. GC-coupled AAS and HPLC-ICP) will be particularly welcome. Manuscripts on other subjects of direct interest to atomic spectroscopists including sample prep- aration and dissolution and analyte pre-concen- tration procedures as well as the statistical interpretation and use of atomic spectrometric data will also be acceptable for publication. There is no page charge. The following types of papers will be considered. Full papers. describing original work. Communications.which must be on an urgent matter and be of obvious scientific importance. Communications receive priority and are usually published within 2-3 months of receipt. They are intended for brief descriptions of work that has progressed to a stage at which it is likely to be valuable to workers faced with similar problems. Reviews. which must be a critical evaluation of the existing state of knowledge on a particular facet of analytical spectrometry. Every paper (except Communications) will be submitted to at least two referees by whose advice the Editorial Board of JAAS will be guided as to its acceptance or rejection. Papers that are accepted must not be published elsewhere except by permission. Submission of a manuscript will be regarded as an undertaking that the same material is not being considered for publication by another journal.Manuscripts (three copies typed in double spacing) should be sent to Brenda Holliday Managing Editor JAAS Dr. J. M. Harnly US Associate Editor JAAS or Prof. N. Furuita Asian- Pacific Editor JAAS. All queries relating to the presentation and sub- mission of papers and any correspondence regarding accepted papers and proofs should be directed to the Editor or US Editor (addresses as above). Members of the JAAS Editorial Board (who may be contacted directly or vra the Editorial Office) would welcome comments suggestions and advice on general policy matters concerning JAAS. Fifty reprints are supplied free of charge. Journal of Amlytrcal Atomc Spectrometry (JAAS) (ISSN 0267-9477) is published monthly by The Royal Society of Chemistry Thomas Graham House Science Park Milton Road Cambridge CB4 4WF UK All orders accompanied with payment should be sent directly to The Royal Society of Chemistry Turpin Distribution Services Ltd Blackhorse Road.Letchworth Herts SG6 lHN UK Tel t 44 (0) 1462 672555; Telex 825372 Turpin G; Fax t 44 (0) 1462 480947 Turpin Distribution Services Ltd. is wholly owned by The Royal Society of Chemistry 1996 Annual subscription rate EEA f599 00 USA $1136.00 Rest of World f1136 00 Customers should make payments by cheque in sterling payable on a UK clearing bank or in US dollars payable on a US clearing bank Air freight and mailing in the USA by Publications Expediting Inc 200 Meacham Avenue Elmont NY 11 003 USA Postmaster send address changes to Journal o f Analytcal Atomrc Spectrometry (JAAS) Publications Expediting Inc.200 Meacham Avenue Elmont NY 11 003 Postage paid at Jamaica. NY 11431. All other despatches outside the UK by Bulk Airmail within Europe Accelerated Surface Post outside Europe PRINTED IN THE UK OThe Royal Society of chemistry 1995 All rights reserved. No part of this publication may be reproduced stored in a retrieval system or transmitted in any form. or by any means electronic mechanical. photographic recording or otherwise without the prior permission of the publishersJournal of Analytical Atomic Spectrometry JAAS Editorial Board Chairman B. L. Sharp (Loughborough UK) A. T. Ellis (Abingdon UK) B. P. Holliday (Cambridge UK) S. J. Haswell (Hull UK) S. J.Hill (Plymouth UK) R. C. Hutton (Cheshire UK) D. Littlejohn (Glasgow UK) H. Crews (Norwich UK) A. Sanz-Medel (Oviedo Spain) P. D. P. Taylor (Gee/ Belgium) JAAS Advisory Board F. C. Adams (Antwerp Belgium) R. M. Barnes (Amherst MA USA) L. Bezur (Budapest Hungary) M. W. Blades (Vancouver Canada) R. F. Browner (Atlanta GA USA) J. L. Burguera (Merida Venezuela) S. Caroli (Rome Italy) J. A. Caruso (Cincinnati OH USA) H. M. Crews (Norwich UK) A. J. Curtius (Norianopolis Brazil) J. B. Dawson (Leeds UK) M. T. C. de Loos-Vollebregt (Delft The Netherlands) 0. F. X. Donard (Talence France) L. Ebdon (Plymouth UK) M. S. Epstein (Gaithersburg MD USA) Fang Zhao-lun (Shenyang China) W. Frech (Umei Sweden) A. K. Gilmutdinov (Uberlingen Germany) G. M. Hieftje (Bloomington IN USA) R.S. Houk (Ames /A USA) R. Klockenkamper (Dortmund Germany) B. V. Cvov (St. Petersburg Russia) R. K. Marcus (Clemson SC USA) J. M. Mermet (Vilieurbanne France) T. Nakahara (Osaka Japan) Ni Zhe-ming (Beuing China) J. W. Olesik (Columbus OH USA) N. Omenetto (lspra Italy) C. J. Park (Taejon Korea) P. J. Potts (Milton Keynes UK) R. E. Sturgeon (Ottawa Canada) V. Sychra (Prague Czech Republic) P. Van Espen (Antwerp Belgium) R. Van Gr.ieken (Antwerp Belgium) B. Welz (Uberlingen Germany) Atomic Spectrometry Updates Editorial Board Chairman *A. T. Ellis (Abingdon UK) J. A. Armstrong (Edinburgh UK) *J. R. Bacon (Aberdeen UK) R. M. Barnes (Amherst MA USA) S. Branch (High Wycombe U K ) R. Bye (Oslo Norway) J. Carroll (Middlesbrough UK) M. R. Cave (Keyworth UK) S. R. N. Chenery (Keyworth UK) *J.M. Cook (Keyworth UK) *M. S. Cresser (Aberdeen UK) H. M. Crews (Norwich UK) J. S. Crighton (Sunbury-on-Thames UK) +J. 6. Dawson (Leeds UK) J. R. Dean (Newcastle upon Tyne UK) *E. H. Evans (Plymouth UK) J. Fazakas (Budapest Hungary) A. Fisher (Plymouth UK) L. M. Garden (Middlesbrough UK) *J M. Gordon (Cambridge UK) D. J. Halls (Glasgow UK) *S. J. Hill (Plymouth UK) K. W. Jackson (Albany NY USA) R. Jowitt (Middlesbrough UK) K. Kitagawa (Nagoya Japan) J. Kubova (Bratislava Slovak Republic) *J. Marshall (Middlesbrough UK) H. Matusiewicz (Poznan Poland) A. W. McMahon (Manchester UK) J. M. Mermet (Villeurbanne France) R. G. Michel (Storrs CT USA) *D. L. Miles (Keyworth UK) T. Nakahara (Osaka Japan) Ni Zhe-ming (BeQing China) P. J. Potts (Milton Keynes UK) W.J. Price (Budleigh Salterton OK) C. J. Rademeyer (Pretoria South Africa) A. Sanz-Medel (Oviedo Spain) *B. L. Sharp (Loughborough UK) I. L. Shuttler (Uberlingen Germany) S. T. Sparkes (Taunton UK) R. Stephens (Halifax Canada) J. Stupar (Ljubljana Slovenia) R. E. Sturgeon (Ottawa Canada) *A. Taylor (Guildford UK) G. C. Turk (Gaithersburg MD USA) J. F. Tyson (Amherst MA USA) P. J. Watkins (London UK) B. Welz (Uberlingen Germany) M. White (lspra Italy) J. G. Williams (Egham UK) J. B. Willis (Victoria Australia) *Members of the ASU Executive Committee Managing Editor JAAS Brenda Holliday The Royal Society of Chemistry Thomas Graham House Science Park Milton Road Cambridge C64 4WF UK. Telephone +44 (0) 1223 420066. Fax +44 (0) 1223 420247. E-mail RSC1 @RSC.ORG (Internet) Production Manager Janice Gordon Publishing Staff Sarah Williams Production Editorial Staff Yasmin Khan Caroline Seeley Ziva Whitelock Roger Young Editorial Secretaries Lesley Turney Claire Harris Frances Thomson US Associate Editor JAAS Dr.J. M. Harnly US Department of Agriculture Beltsville Human Nutrition Research Center Beltsville MD 20705 USA. Telephone + 1 301 -504-8569 Asia-Pacific Associate Editor JAAS Prof. N. Furuta Department of Applied Chemistry Faculty of Science and Engineering Chuo University 1-1 3-27 Kasuga Bunkyo-ku Tokyo 11 2 Japan. Telephone 81 -3-381 7-1 906. Fax 81 -3-381 7-1 895. E-mail nfuruta@apchem.chem.chuo-u.ac.jp Advertisements Advertisement Department The Royal Society of Chemistry Burlington House Piccadilly London W1 V OBN UK.Telephone + 44 (0) 171 -287 3091. Fax + 44 (0) 171 -494 11 34. Information for Authors Full details of how to submit materials for publi- cation in JAAS are given in the Instructions to Authors in Issue 1. Separate copies are available on request. The Journal of Analytical Atomic Spectrometry (JAAS) is an international journal for the publi- cation of original research papers communi- cations and letters concerned with the development and analytical application of atomic spectrometric techniques. The journal is pub- lished twelve times a year including comprehen- sive reviews of specific topics of interest to practising atomic spectroscopists and incorpor- ates the literature reviews which were previously published in Annual Reports on Analytical Atomic Spectroscopy (ARAAS).Manuscripts intended for publication must describe original work related to atomic spectro- metric analysis. Papers on all aspects of the sub- ject will be accepted including fundamental studies novel instrument developments and prac- tical analytical applications. As well as AAS AES and AFS papers will be welcomed on atomic mass spectrometry X-ray fluorescence/ernission spectrometry and secondary emission spec- trometry. Papers describing the measurement of molecular species where these relate to the characterization of sources normally used for the production of atoms or are concerned for example with indirect methods of analysis will also be acceptable for publication. Papers describing the development and applications of hybrid techniques (e.g.GC-coupled AAS and HPLC-ICP) will be particularly welcome. Manuscripts on other subjects of direct interest to atomic spectroscopists including sample prep- aration and dissolution and analyte pre-concen- tration procedures as well as the statistical interpretation and use of atomic spectrometric data will also be acceptable for publication. There is no page charge. The following types of papers will be considered. Full papers describing original work. Communications which must be on an urgent matter and be of obvious scientific importance. Communications receive priority and are usuaNy published within 2-3 months of receipt. They are intended for brief descriptions of work that has progressed to a stage at which it is likely to be valuable to workers faced with similar problems.Reviews which must be a critical evaluation of the existing state of knowledge on a particular facet of analytical spectrometry. Every paper (except Communications) will be submitted to at least two referees by whose advice the Editorial Board of JAAS will be guided as to its acceptance or rejection. Papers that are accepted must not be published elsewhere except by permission. Submission of a manuscript will be regarded as an undertaking that the same material is not being considered for publication by another journal. Manuscripts (three copies typed in double spacing) should be sent to Brenda Holliday Managing Editor JAAS Dr. J. M. Harnly US Associate Editor JAAS or Prof. N. Furuita Asian- Pacific Editor JAAS. All queries relating to the presentation and sub- mission of papers and any correspondence regarding accepted papers and proofs should be directed to the Editor or US Editor (addresses as above).Members of the JAAS Editorial Board (who may be contacted directly or via the Editorial Office) would welcome comments suggestions and advice on general policy matters concerning JAAS . Fifty reprints are supplied free of charge. Journal of Analytical Atomic Spectrometry (JAAS) (ISSN 0267-9477) is published monthly by The Royal Society of Chemistry Thomas Graham House Science Park Milton Road Cambridge CB4 4WF UK. All orders accompanied with payment should be sent directly to The Royal Society of Chemistry Turpin Distribution Services Ltd. Blackhorse Road Letchworth Herts. SG6 lHN UK Tel. +44 (0) 1462 672555; Telex 825372 Turpin G; Fax -1-44 (0) 1462 480947. Turpin Distribution Services Ltd. is wholly owned by The Royal Society of Chemistry. 1996 Annual subscription rate EEA f599.00 USA $1 136.00 Rest of World fll36.00. Customers should make payments by cheque in sterling payable on a UK clearing bank or in US dollars payable on a US clearing bank. Air freight and mailing in the USA by Publications Expediting Inc. 200 Meacham Avenue Elmont NY 1 1 003. USA Postmaster send address changes to Journal of Analytical Atomic Spectrometry (JAAS) Publications Expediting Inc. 200 Meacham Avenue Elmont NY 11 003. Postage paid at Jamaica NY 11431. All other despatches outside the UK by Bulk Airmail within Europe Accelerated Surface Post outside Europe. PRINTED IN THE UK. @The Royal Society of Chemistry 1995. All rights reserved. No part of this publication may be reproduced stored in a retrieval system or transmitted in any form or by any means electronic mechanical photographic recording or otherwise without the prior permission of the publishers.
ISSN:0267-9477
DOI:10.1039/JA99510FX061
出版商:RSC
年代:1995
数据来源: RSC
|
4. |
Contents pages |
|
Journal of Analytical Atomic Spectrometry,
Volume 10,
Issue 11,
1995,
Page 063-064
Preview
|
PDF (886KB)
|
|
摘要:
Journal of Analytical Atomic Spectrometry 1 111111111111111111 1 . ___ ._. . __ JASPE2 lO(11) 59N-61 N 905-1 032 329R-358R (1995) I CONTENTS NEWS PAGES Book Reviews Diary of Conferences and Courses Future Issues 59N 59N 61 N PAPERS Characterization of Ionization and Matrix Suppression in Inductively Coupled Cold’ Plasma Mass Spectrometry Scott D. Tanner Spectroscopic Method for the Determination of the Electron Temperature in Quasi-thermal Air Discharges. Application to an Inductively Coupled Air Plasma at Atmospheric Pressure Anne-Marie Gomes Jean-Philippe Sarrette Lydie Madon Arnaud Epifanie Application of Multi-element Time-resolved Analysis to a Rapid On-line Matrix Separation System for Inductively Coupled Plasma Mass Spectrometry Simon M. Nelms Gillian M. Greenway Robert C.Hutton Computer Simulation of Enclosed Inductively Coupled Plasma Discharges. Part 1. Monatomic Gases Ana Gaillat Ramon M. Barnes Pierre Proulx Maher 1. Boulos Computer Simulation of Enclosed Inductively Coupled Plasma Discharges. Part 2. Molecular Gases Ana Gaillat Ramon M. Barnes Pierre Proulx Maher I. Boulos Determination of Trace Element Impurities in Nuclear Materials by Inductively Coupled Plasma Mass Spectrometry in a Glove-box Zlatan Kopajtic Stefan Rollin Beat Wernli Chantal Hochstrasser Guido Ledergerber Petr Jurcek Determination of Boron Using Mannitol-assisted Electrothermal Vaporization for Sample Introduction in Inductively Coupled Plasma Mass Spectrometry Wen-Ching Wei Chih-Jung Chen Mo-Hsiung Yang Hydride Generation Inductively Coupled Plasma Mass Spectrometric Detection of Lead Compounds Separated by Liquid Chromatography Hueih-Jen Yang Shiuh-Jen Jiang Determination of Antimony by Continuous Hydride Generation Coupled with Non-dispersive Atomic Fluorescence Detection Alessandro O’Ulivo Leonard0 Lampugnani Giovanna Pellegrini Roberto Zamboni Interpretation of the Interference Mechanisms Occurring in the Determination of Antimony(ll1) by Hydride Generation Atomic Absorption Spectrometry Based on Normal Reduction Potentials M.Teresa Martinez-Soria Jesus Sanz Asensio J. Galban Bernal Continuous-flow Microwave-assisted Digestion of Environmental Samples Using Atomic Spectrometric Detection Ralph E. Sturgeon Scott N. Willie Brad A. Methven Joseph W. H. Lam Henryk Matusiewicz Determination of Cadmium at Ultratrace Levels by Cold Vapour Atomic Absorption Spectrometry Guo Xiao-Wei Guo Xu-Ming Noise Studies for Detection Limits for Some Electrothermal Atomic Absorption Determinations and Calculation of the Optimal Detection Limit from One Atomization A.Le Bihan H. Le Garrec J. Y. Cabon Y. Guern Determination of Silicon in Electrolyte Solutions by Electrothermal Atomic Absorption Spectrometry Using Platinum as a Chemical Modifier Masami Fukushima Toshio Ogata Kensaku Haraguchi Kohichi Nakagawa Saburo Ito Masao Sumi Naoto Asami 905 923 929 935 94 1 947 955 963 969 975 98 I 987 993 999 continued on inside back cove1 lllllllllllllllll “1267 - 9 ~ 7 7 ( 1995 1 1 1 1 - A Typeset printed and bound by The Charlesworth Group Huddersfield England. 01484 517077Thermally Stabilized Iridium on an Integrated Carbide-coated Platform as a Permanent Modifier for Hydride-forming Elements in Electrothermal Atomic Absorption Spectrometry Dimiter L.Tsalev Alessandro D’Ulivo Leonard0 Lampugnani Marco Di Marco Roberto Zamboni Direct Determination of Nickel in Heroin and Cocaine by Electrothermal Atomic Absorption Spectrometry Using Deuterium Arc Background Correction Combined with Chemical Modification Pilar Bermejo-Barrera Antonio Moreda- PiAeiro Jorge Moreda-PiAeiro Adela Bermejo-Barrera Direct Coupling of High-performance Liquid Chromatography to Microwave- induced Plasma Atomic Emission Spectrometry via Volatile-species Generation and Its Application to Mercury and Arsenic Speciation Jose M. Costa-Fernandez Florian Lunzer Rosario Pereiro-Garcia Alfredo Sanz-Medel Nerea Bordel-Garcia Assessment of Direct Solid Sample Analysis by Graphite Pellet Electrothermal Vaporization Inductively Coupled Plasma Mass Spectrometry J. M. Ren R. Rattray Eric D. Salin D. Conrad Gregoire CUMULATIVE AUTHOR INDEX 1003 101 1 1019 1027 1031 ATOMIC SPECTROMETRY UPDATES References 329R
ISSN:0267-9477
DOI:10.1039/JA99510BX063
出版商:RSC
年代:1995
数据来源: RSC
|
5. |
Atomic Spectrometry Updates—References |
|
Journal of Analytical Atomic Spectrometry,
Volume 10,
Issue 11,
1995,
Page 329-358
Preview
|
PDF (5379KB)
|
|
摘要:
ATOMIC SPECTROMETRY UPDATES-REFERENCES 9513362 9513363 9513364 9513365 9513366 9513367 9513368 9513369 9513370 951337 1 9513372 9513373 9513374 Denoyer E. R. Jacques D. Debrah D. Tanner S. D. Determination of trace elements in uranium practical benefits of a new ICP-MS lens system. At. Spectrosc. 1995 16 1. (Perkin-Elmer Corp. Norwalk CT Tanner S. D. Paul M. Beres S. A. Denoyer E. R. Application of cold plasma conditions for the determi- nation of trace levels of iron calcium potassium sodium and lithium by ICP-MS. At. Spectrosc. 1995 16 16. (SCIEX Thornhill Ontario Canada L3T lP2). Wolf R. E. Denoyer E. R. Design and performance criteria for a new ICP-MS for environmental analysis. At. Spectrosc. 1995 16 22. (Perkin-Elmer Corp. Norwalk CT USA). Lust A. Atomic spectroscopy bibliography for July- December 1994.At. Spectrosc. 1995 16 28. (Perkin- Elmer Corp. Norwalk CT USA). Gray D. J. Wang S. Brown R. Stability and sensitivity enhancement using ETV-ICP-MS. Appl. Spectrosc. 1994 48 1316. (Elemental Res. Inc. Vancouver British Columbia Canada V7M 1A5). Yap C. T. Hua Y. Experimental studies in EDXRF on a new linear relationship for fluorescence. Appl. Spectrosc. 1994 48 1394. (Dept. Phys. Natl. Univ. Singapore Singapore 051 1 Singapore). Goode S. R. Thomas C. Gas chromatography interfaced to atomic-emission spectrometry. Separation identification and quantitation. Spectroscopy (Eugene Oreg.) 1994 9 14. (Dept. Chem. and Biochem. Univ. South Carolina Columbia SC 29208 USA). Sneddon J. Smith M. V. Indurthy S. Lee Y. Direct and near-real-time multielement determination of metals in aerosols by impaction-graphite furnace AAS.Spectroscopy (Eugene Oreg.) 1995 10 26. (Dept. Chem. McNeese State Univ. Lake Charles LA 70609 USA). Hiraide M. Ishikawa K. Chen Z. S. Kawaguchi H. Coprecipitation with metal hydroxides for the determi- nation of beryllium in sea water by graphite furnace atomic absorption spectrometry. Mikrochim. Acta 1994 117 7. (Dept. Mater. Sci. and Eng. Nagoya Univ. Nagoya 464 Japan). Bermejo Barrera P. Lorenzo Alonso M. J. Aboal Somoza M. Bermejo Barrera A. Determination of arsenic in mussels by slurry sampling and electrothermal atomic absorption spectrometry (ETAAS). Mikrochim. Acta 1994 117 49. (Dept. Anal. Chem. Nutr. and Bromatol. Fac. Chem. Univ. Santiago de Compostela 15706 Santiago de Compostela Spain).Resende Boaventura G. da Rocha Hirson J. Erthal Santelli R. Determination of molybdenum in silicates by flame atomic absorption spectrometry exploiting activated carbon as collector. Fresenius ’ J. Anal. Chem. 1994 350 651. (Geosci. Inst. Univ. Brasilia Brasilia Brazil). Siemens V. Harju T. Laitinen T. Larjava K. Broekaert J. A. C. Applicability of microwave-induced plasma optical emission spectrometry (MIP-OES) for continuous monitoring of mercury in flue gases. Fresenius’ J. Anal. Chem. 1995 351 11. (Inst. Spectrochem. and Appl. Spectrosc. 44139 Dortmund Germany). Voulgaropoulos A Ayiannidis A. Stratis J. Zachariadis G. Giroussi S. Atomic absorption spectro- scopic determination of molybdenum in aqueous tetra- thiomolybdate solutions.Fresenius’ J. Anal. Chem. 1995 351 139. (Lab. Anal. Chem. Dept. Chem. 06859-0215 USA). 9513375 9513376 9513377 9513378 9513 379 9513380 9513381 9513382 95/33 83 9 513 3 84 951338 5 9513 386 Aristotle Univ. 54006 Thessaloniki Macedonia Greece). Oreshkin V. N. Tsizin G. I. Vnukovskaya G. L. Sorption atomic absorption determination of metal traces (silver bismuth indium cadmium lead and thallium) in natural waters using double-chamber powder atomizer. Zh. Anal. Khim. 1994 49 755. (Inst. Soil Sci. and Photosynthesis Russian Acad. Sci. Pushchino Russia). Shimizu T. Fukuda K. Shijo Y. Graphite furnace AAS determination of silver in sea water after solvent extraction and back extraction. Bunseki Kagaku 1994 43 1009. (Dept. Appl. Chem. Fac. Eng. Utsunomiya Univ. Utsonumiya Tochigi 321 Japan). Hirayama K.Sekine T. Unohara N. Determination of trace aluminium in natural waters by ICP-AES after separation and preconcentration with use of Chrome Azurol S immobilized on silica gel. Bunseki Kagaku 1994 43 1065. (Dept. Ind. Chem. Coll. Eng. Nihon Univ. Koriyama Fukushima 963 Japan). Suzuki Y. Shirasaki T. Nakaguchi Y. Koike Y. Hiraki K. Determination of molybdenum in natural water by solvent extraction and ICP-AES. Bunseki Kagaku 1994 43 1127. (Dept. Chem. Fac. Sci. and Technol. Kinki Univ. Higashiosaka Osaka 577 Japan). Shirasaki T. Nakamura H. Hiraki K. Determination of lead in river water by graphite furnace AAS with cobalt(I1 nitrate-ammonium dihydrogen phosphate as matrix modifier. Bunseki Kagaku 1994 43 1149. (Techno-res. Lab.Hitachi Instrument Eng. Co. Ltd. Katsuta Ibaraki 3 12 Japan). Kawai H. Katayama Y. Ninomiya Y. Okuda J. Determination of trace metals in poly(ethy1ene tereph- thalate) film by punched-out film introduction and graphite furnace AAS. Bunseki Kagaku 1994 43 1193. (Ashigara Res. Lab. Fuji Photo Film Co. Ltd. Minami- Ashigara Kanagawa 250-01 Japan). Shida J. Mochizuki J. Matsuzaki S. Determination of gallium by graphte furnace AAS with one-resin- bead insertion after retention with tiron on a uniform anion-exchange resin. Bunseki Kagaku 1994 43 1197. (Dept. Mater. Sci. and Eng. Fac. Eng. Yamagata Univ. Yonezawa Yamagata 992 Japan). Peng L.-q Yao J.-y. Direct determination of selenium in high temperature nickel-based alloy by hydride generation graphite furnace atomic absorption spec- trometry.Fenxi Huaxue 1994 22 1135. (Changchun Inst. Appl. Chem. Chinese Acad. Sci. Changchun 130022 China). Long X.-l. Xie G.-m. Study on the separation and preconcentration of palladium with foam plastics loaded with hydrosulfurylcarbon powder and its application. Fenxi Shiyanshi 1994 13 28. (Dept. Appl. Chem. Chengdu Inst. Technol. Chengdu 610059 China). Chi K. Gao Y.-q. Determination of lead in water by a micro-amount flame atomic absorption technique. Fenxi Shiyanshi 1994 13 52. (Beijing General Res. Inst. Non-Ferrous Metals Beijing 100088 China). Wang S.-z. Gong C.-s. Determination of tin in geochemical samples and lead by slip-type quartz tube hydride generation atomic absorption spectrophoto- metry. Lihua Jianyan Huaxue Fence 1994 30 329.(Northwest Nonferrous Geol. Res. Inst. Xi’an 710054 China). Xuan W.-k. Ye M.-h. Rapid GFAAS determination of micro-amounts of cadmium in cobalt metal and sea Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 329R9513387 9513388 9513 389 9513390 9513391 9513392 9513393 9513394 9513395 9513396 9513 397 9513398 9 5/3 399 330 R water. Lihua Jianyan Huaxue Fence 1994 30 341. (Shanghai Res. Inst. Steels Shanghai 200940 China). Cao W.-h. Ying H. AES determination of yttrium niobium zirconium lanthanum manganese titanium beryllium chromium and vanadium in geological samples using shallow hole electrodes. Lihua Jianyan Huaxue Fence 1994 30 345. (Jiangxi Inst. Phys. and Chem. Miner. Explor. Nanchang 330201 China). Shi Y.-k. Wei Y.-w. FAAS determination of manganese in polymer aluminium chloride.Lihua Jianyan Huaxue Fence 1994 30 368. (Nantong Municipal Sanitation and Anti-Epidemic Stn. Nantong 226006 China). Ma X.-g. Zhang Z.-x. Qian H.-w. Elimination of spectral interference in ICP-AES by a computer spectrum-stripping method. Guangpuxue Yu Guangpu Fenxi 1994,14(4) 55. (Dept. Chem. Zhongshan Univ. Guangzhou 510275 China). Wu M.-s. Shao H.-x. Study of the influence of ICP- AES operating conditions and hydride generation conditions on the spectral signals of arsenic selenium and germanium. Guangpuxue Yu Guangpu Fenxi 1994 14(4) 63. (Suzhou Univ. Suzhou 215006 China). Peng X.-j. Jiang Z.-c. Zeng Y.-e. Desolvation in an ICP-AES system by on-line column preconcentration and flow-injection analysis. Guangpuxue Yu Guangpu Fenxi 1994 14(4) 71.(Dept. Chem. Wuhan Univ. Wuhan 430072 China). Yan X.-p. Ni Z.-m. Progress in thermodynamic and kinetic studies on the mechanism of atom formation in electrothermal atomic absorption spectrophotometry. Guangpuxue Yu Guangpu Fenxi 1994 14(4) 79. (Res. Centre Eco-Environ. Sci. Acad. Sin. Beijing 100085 China). Zhang J.-m. Chen H. Zhang Q. Studies on some features of special hollow-cathode lamps for hydride generation non-dispersive atomic fluorescence spectro- photometry. Guangpuxue Yu Guangpu Fenxi 1994 14(4) 89. (Inst. Geophys. and Geochem. Explor. Langfang 102849 Hebei China). Sun X. Huang F.-x. Mei W.-d. Determination of trace nickel in the serum of cancer patients by graphite furnace atomic absorption spectrophotometry with use of ammonium vanadate and lanthanum as matrix modifiers with molybdate-coated tubes.Guangpuxue Yu Guangpu Fenxi 1994 14(4) 97. (Oncol. Lab. First Affiliated Hosp. Anhui Med. Univ. Hefei 230033 China). Lai J.-p. Study of interference on the determination of aluminium by nitrous oxide-acetylene flame AAS. Guangpuxue Yu Guangpu Fenxi 1994 14(4) 101. (Zhanjiang Teacher’s Coll. Zhanjiang 524048 China). Cheo W.-h. Xiong G.-p. Preparation of solvent- impregnated filter papers and their application to XRF analysis. 11. Study on the method of preparing disc specimens by using solvent-impregnated filter papers in XRF analysis. Guangpuxue Yu Guangpu Fenxi 1994 14( 4) 107. (Cuangzhou Branch Inst. Geochem. Acad. Sin. Guangzhou 510640 China). Revenko A. G. Sample preparation of naturally occur- ring materials for XRF energy-dispersion analysis.Overview. Zavod. Lab. 1994 60 16. (Russia). Pagano S. T. Smith B W. Windfordner J. D. Determination of mercury in microwave-digested soil by laser-excited atomic fluorescence spectrometry with electrothermal atomization. Talanta 1994 41 2073. (Dept. Chem. Univ. Florida Gainesville FL 3261 1 USA). Fuh M.-R. S. Rochefort W. E. Analysis of residual phosphorus in poly( p-phenylene benzoxazole) PBO film by X-ray fuorescence (XRF) spectrometry. Talanta 1994,41,2087. (Dept. Chem. Soochow Univ. Shih Lin Taipei Taiwan). 95/3400 9 51340 1 9513402 9513403 9513404 9513405 9513406 9513407 9513408 9513409 9513410 951341 1 9513412 9513413 Wu Q.-c. Wang N.-x. Lu HA. Shi J.-b. New equation for wavelength-dispersive X-ray fluorescence analysis without standards.Talanta 1994 41 2121. (Shandong Anal. and Test Centre Jihan 250014 China). Fang Z.4 Xu S.-k. Dong L.-p. Li W.-q. Determination of cadmium in biological materials by flame atomic absorption spectrometry with flow injec- tion on-line sorption preconcentration. Talanta 1994 41 2165. (Flow Injection Anal. Res. Centre Inst. Appl. Ecol. Acad. Sin. Shenyang 110015 China). Carvalho M. S. Medeiros J. A. Nobrega A. W. Mantovano J. L. Rocha V. P. A. Direct determination of gallium on polyurethane foam by X-ray fluorescence. Talanta 1995 42 45. (Inst. Eng. Nucl. Comm. Nacl. Energia Nucl. Cidade Univ. Rio de Janeiro 21945-970 Brazil). Masseau S. Dall’Ava D. Bergey C. Ablation laser couplage to plasma torch atomic emission spectrometry in a glove box.Analusis 1994 22 445. (DAM/ Centre Etudes Valduc Comm. Energ. At. 21120 Is-sur- Tille France). Detcheva A. Havesov I. Controlled dispersion flow analysis devices with constant flow for flame atomic absorption spectrometry. Analusis 1994 22 453. (Inst. Gen. Inorg. Chem. Bulgarian Acad. Sci. Sofia 1113 Bulgaria). Koshino Y. Narukawa A. Rarnan spectrometric study of the charring process of lead in sulfur in electrothermal atomic absorption spectrometry. Analyst (London) 1994 119,2473. (Mater. Res. Lab. Corp. Res. and Dev. Group Aichi 467 Japan). Corns W. T. Stockwell P. B. Jameel M. Rapid method for the determination of total mercury in urine samples using cold vapour atomic fluorescence spec- trometry. Analyst (London) 1994 119 2481. ( P S Analytical Ltd.Sevenoaks Kent UK TN15 6QY). Ossaka T. Kakegawa K. Oi T. Mukaida M. Major- element analysis of selected rock and volcanic ash samples in the Unzen area Japan by X-ray fluorescence spectroscopy. J. Radioanal. Nucl. Chem. 1994 183 235. (Dept. Chem. Sophia Univ. Chiyoda Tokyo 102 Japan). Baimonda D. Bernasconi G. Haselberger N Markowicz A. Valkovic V. Trace element XRF analysis of Mongolian coals. J. Radioanal. Nucl. Chem. 1994 185 27. (IAEA Lab. 2444 Seibersdorf Austria). Jenkins S. N. Castle J. E. Development and practical application of a transmission X-ray photoelectron spectrometer. Surf. Interface Anal. 1994,21 382. (Dept. Mater. Sci. and Eng. Univ. Surrey Guildford Surrey UK GU2 5XH). Knoth J. Schneider H. Schwenke H. Tunable excit- ing energies for total-reflection X-ray fluorescence spectrometry using a tungsten .anode and bandpass filtering. X-Ray Spectrom.1994 23 261. (GKSS- Forschungszentrum 21494 Geesthacht Germany). Metz U. Hoffmann P. Weinbruch S. Ortner H. M. Comparison of X-ray fluorescence spectrometric (XRF) techniques for the determination of metal traces especially in plastics. Mikrochim. Acta 1994 117 95. (Fac. Mater. Fachgebiet Chem. Anal. Tech. Hochschule 64295 Darmstadt Germany). dos Santos J. M. F. Bento A. C. S. S. M. Conde C. A. N. Performance of the curved-grid gas proportional scintillation counter in X-ray spectrometry. Nucl. Instrum. Methods Phys. Res. Sect. A 1994 337 427. (Phys. Dept. Univ. Coimbra 3000 Coimbra Portugal). Wang J. Marshall W. D. Metal speciation by supercritical-fluid extraction with on-line detection by atomic absorption spectrometry.Anal. Chem. 1994 66 3900. (Dept. Food Sci. and Agric. Chem. McGill Univ. Ste. Anne de Bellevue Canada H9X 3V9). Journal of Analytical Atomic Spectrometry November 1995 Vol. 1095/34 95/34 95/3416 9513417 9513418 95/34 19 9513420 9513421 9513422 9513423 9513424 9 513425 9513426 9513427 9513428 You J. Z. Fanning J. C. Marcus R. K. Particle-beam aqueous sample introduction for hollow-cathode atomic emission spectroscopy. Anal. Chem. 1994 66 39 16. (Howard L. Hunter Chem. Lab. Dept. Chem. Clemson Univ. Clemson SC 29634-1905 USA). Israel Y. Barnes R. M. Flow-injection dispersion characteristics with inductively coupled plasma atomic emission spectrometry. 2. Influence of flow modes and manifold configuration.Anal. Chem. 1994 66 3937. (Dept. Chem. Lederle Grad. Res. Centre Univ. Massachusetts Amherst MA 01003-4510 USA). Bahnick D. Sauer C. Butterworth B. C. Kuehl D. W. National study of mercury contamination of fish. IV Analytical methods and results. Chemosphere 1994 29 537. (Centre Lake Superior Environ. Studies Univ. Superior Superior WI 54880 USA). Qiu D. Recent advances in fundamental studies of hydride generation. TrAC Trends Anal. Chem. (Pers. Ed.) 1995,14,76. (Chem. Dept. Fudan Univ. Shanghai 200433 China). Muller J. F. Krier G. Chamel A. Laser desorption and its applications in botanical and environmental sciences. J. Trace Microprobe Tech. 1994,12 145. (Lab. Spectrom. Masse et Chim. Laser IPEM 57078 Metz 3 France). Klaos E. G. Non-governmental analytical laboratory experience and problems.Zauod. Lab. 1994 60 9. (NITS Vartek Vartek Int. Co. Takllinn Estonia). Standards Australia Methods for the analysis of zinc and zinc alloys. Part 2 determination of magnesium content - flame atomic absorption spectrometric method. Australian Standards AS 1329.2- 1994 1994 12. (1 The Crescent Homebush NSW 2140 Australia). Standards Australia Methods for the analysis of zinc and zinc alloys. Part 3 determination of aluminium content - flame atomic absorption spectrometric method. Australian Standards AS 1329.3- 1994 1994 12. (1 The Crescent Homebush NSW 2140 Australia). Standards Australia Methods for the analysis of zinc and zinc alloys. Part 5 determination of copper content (0.0001% to 0.0025%) - flame atomic absorption spectrometric method.Australian Standards AS 1329.5-1994 1994 12. (1 The Crescent Homebush NSW 2140 Australia). Standards Australia Methods for the analysis of zinc and zinc alloys. Part 6 determination of copper content (0.25% to 1.25%) - flame atomic absorption spectro- metric method. Australian Standards AS 1329.6- 1994 1994 12. (1 The Crescent Homebush NSW 2140 Australia). Standards Australia Methods for the analysis of zinc and zinc alloys. Part 7 determination of lead content - flame atomic absorption spectrometric method. Standards Australia AS 1329.7-1994 1994 12. (1 The Crescent Homebush NSW 2140 Australia). Standards Australia Methods for the analysis of zinc and zinc alloys. Part 8 determination of cadmium content - flame atomic absorption spectrometric method.Australian Standards AS 1329.8- 1994 1994 12. (1 The Crescent Homebush NSW 2140 Australia). Standards Australia Copper alloys. Part 1 determi- nation of lead in copper alloys (flame atomic absorption spectrometric method). Australian Standards AS 1515.1-1994 1994 12. (1 The Crescent Homebush NSW 2140 Australia). Standards Australia Copper alloys. Part 2 determi- nation of manganese content - flame atomic absorp- tion spectrometric method. Australian Standards AS 1515.2-1994 1994 12. (1 The Crescent Homebush NSW 2140 Australia). Gorlova M. N. Skorskaya 0. L. Fridman G. I. Novel use of the addition method in the determination of 95/3429 95/3430 951343 1 9513432 9 5/343 3 9.513434 95/3435 9513436 9513437 9513438 9 51343 9 9513440 9513441 trace elements by atomic spectroscopy.Zauod. Lab. 1994 60( 12) 19. (Vserossiiskii Inst. Legkikh Splavov Moscow Russia). Ivanov A. A. Lazarev A. I. Gerko V. V. Attachment to an atomic absorption spectrophotometer for spectro- photometry. Zauod. Lab. 1994 60( 12) 26. (Inst. New Chem. Problems Russian Acad. Sci. Chernogolovka Moscow Region Russia). Yudelevich I. G. Petrova N. I. Buyanova L. M. Determination of antimony and iron impurities in high- purity gallium by atomic absorption spectrometry with electrothermal atomization. Vysokochist. Veshchestua 1994 121. (Inst. Inorg. Chem. Siberian Div. Russian Acad. Sci. Novosibirsk Russia). Shelpakova I. R. Beizel’ N. F. Kosyakov V. I. Komissarova L. N. Zaksas B. I. Technique for quantitative atomic absorption determination of arsenic in high-purity cadmium with concentration by sample base distillation. Vysokochist.Veshchestva 1994 125. (Inst. Inorg. Chem. Siberian Div. Russian Acad. Sci. Novosibirsk Russia). Saito M. Relative sensitivity factors in direct-current glow-discharge mass spectrometry using krypton and xenon gas - estimation of the role of Penning ionization. Fresenius’ J. Anal. Chem. 1995 351 148. (Mater. Characterization Div. Natl. Res. Inst. Metals Tsukuba Ibaraki 305 Japan). Nickel H. Zadgorska Z. Strategy for calibrating direct ETV-ICP-OES analysis of industrial ceramics in powder form. Fresenius’ J. Anal. Chem. 1995 351 158. (Res. Centre Jiilich Inst. Mater. Energy Syst. 52425 Julich Germany). Sahuquillo A. Lopez-Sanchez J. F. Rubio R. Rauret G. Hatje V. Sequential extraction of trace metals from sediments.I. Validation of chromium determination in the extracts by AAS. Fresenius’ J. Anal. Chem. 1995 351 197. (Dept. Quim. Anal. Univ. Barcelona 08028 Barcelona Spain). Falandysz J. Bona H. Danisiewicz D. Silver content of wild-grown mushrooms from Northern Poland. Z . Lebensm. Unters. Forsch. 1994 119 222. (Environ. Chem. and Toxicol. Res. Group Fac. Chem. Univ. Gdansk 80-952 Gdansk Poland). Wand J.-d. Yu R.-p. Xiao K.-t. Tian L.-q. Application of atomic absorption spectrometry to organic analysis. V. Determination of total amount of acid in soda water. Fenxi Huaxue 1994 22 1289. (Dept. Chem. Xinjiang Univ. Urungi 830046 China). Kawamata Y. Sakurai S. Yoshimoto E. Kitamura T. Sbimizu T. Shijo Y. Determination of trace copper in high-purity aluminium by graphite-furnace AAS after solvent extraction and microscale back extraction.Bunseki Kagaku 1995 44 117. (Dept. Appl. Chem. Fac. Ent. Utsunomiya Univ. Utsunomiya Tochid 321 Japan). Yokota F. Morikawa H. Ishizuka T. Determination of impurities in tantalum carbide and tantalum nitride by high-pressure acid decomposition and ICP-AES. Bunseki Kagaku 1995 44 123. (Ind. Res. Inst. Aichi Prefectural Government Kariya Aichi 448 Japan). Yokota F. Morikawa H. Ishizuka T. Determination of impurities in titanium boride by acid decomposition and ICP-AES. Bunseki Kagaku 1995 44 157. (Ind. Res. Inst. Aichi Prefectural Government Kariya Aichi 448 Japan). Wang X. Zhuang Z. Zhu E. Yang C. Wan T. Yu L. Multi-element ICP-AES analysis of hair samples and a chemometrics study for cancer diagnosis.Microchem. J. 1995,51,5. (Dept. Chem. Xiamen Univ. Xiamen 361005 China). Ba’nhidi O. Paksy L. Software package and some experiences obtained by its use in statistical evaluation Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 331 R9513442 9513443 9513444 9513445 9513446 9513447 9513448 9513449 9513450 951345 1 9513452 9 51345 3 9513454 332R of the results of ICP spectrometry. Microchem. J. 1995 51 15. (Metalcontrol Kft. 3540 Miskolc Hungary). Bozsai G. Melegh M. Application of the transversely heated graphite atomizer to the determination of trace metals in environmental and biomedical samples. Microchem. J. 1995 51 39. (Natl. Inst. Hygiene 1966 Budapest Hungary). Herber R. F. M. Use of solid sampling analysis for the determinaiton of trace elements in tissues.Microchem. J. 1995 51 46. (Coronel Lab. Occup. and Environ. Health Univ. Amsterdam Meibergdreef 15 1105 AZ Amsterdam Netherlands). Gerotto M. Dell’Andrea E. Bortoli A. Marchiori M. Palonta M. Troncon A. Interference effects and their control in ICP-MS analysis of serum and saline solutions. Microchem. J. 1995,51 73. (Environ. Chem. Sect. Presidio Multizonale Prevenzione Via della Montagnola 2 30171 Mestre-Venice Italy). Andrasi E. Orosz L. Bezur L. Ernyei L. Molnar Z. Normal human brain analysis. Microchem. J. 1995 51 99. (Inst. Inorg. and Anal. Chem. L. Eotvos Univ. Budapest 112 Hungary). Dao Thi Phuong D. Tatar E. Varga I. Zaray G. Cseh E. Fodor F. Accumulation and translocation of lead in cucumber plants monitored by graphite furnace atomic absorption spectrometry.Microchem. J. 1995 51 145. (Dept. Inorg. and Anal. Chem. Eotvos Univ. 1518 Budapest Hungary). Fodor P. Bertenyi-Divinyi Z. Uncertainty in environ- mental ICP-AES measurements. Microchem. J. 1995 51,151. (Dept. Chem. and Biochem. Univ. Horticulture and Food Ind. 1118 Budapest Villanyi 35 Hungary). Santarsiero A Ottaviani M. Evaluation of heavy metals in slags from medical waste incinerator. Microchem. J. 1995 51 166. (Inst. Superiore Sanita 00161 Rome Italy). Zaray G. Dao Thi Phuong D. Varga I. Varga A. Kantor T. Cseh E. Fodor F. Influences of lead contamination and complexing agents on the metal uptake of cucumber. Microchem. J. 1995 51 207. (Dept. Inorg. and Anal. Chem. L. Eotvos Univ. 1518 Budapest 112 Hungary).Kantor T. Zaray G. Improved design and optimization of an electrothermal vaporization system for inductively coupled plasma atomic emission spectrometry. Microchem. J. 1995 51 266. (Dept. Inorg. and Anal. Chem. L. Eotvos Univ. 1518 Budapest 112 Hungary). Petit de Pena Y. Gallego M. Valcarcel M. On-line sorbent extraction preconcentration and determination of lead by atomic absorption spectrometry. Talanta 1995 42 211. (Dept. Anal. Chem. Fac. Sci. Univ. Cordoba 14004 Cordoba Spain). Ohta K. Isiyama T. Yokoyama M. Mizuno T. Determination of gold in biological materials by electrothermal atomic absorption spectrometry with a molybdenum tube atomizer. Talanta 1995 42 263. (Dept. Chem. for Mater. Fac. Eng. Mie Univ. Tsu Mie 514 Japan). Sen Gupta J.G. Bouvier J. L. Direct determination of traces of silver cadmium lead bismuth chromium manganese cobalt nickel lithium beryllium copper and antimony in environmental waters and geological materials by simultaneous multi-element graphite fur- nace atomic absorption spectrometry with Zeeman- effect background correction. Talanta 1995 42 269. (Geol. Surv. Canada Ottawa Ontario Canada K1A OES). Dundar M. S. Haswell S. J. Comparison of copper speciation results obtained using electrothermal atomiz- ation atomic absorption spectrometry and computer modelled data. Anal. Proc. (London) 1995 32 133. (Sch. Chem. Univ. Hull Hull UK HU6 7RX). 9513455 9513456 9513457 9513458 9513459 9513460 9513461 9513462 9513463 9513464 9513465 9513466 9513467 9513468 Journal of Analytical Atomic Spectrometry November 1995 Vol.10 Pitts L. Worsfold P. J. Hill S. J. Selenium speci- ation - a flow-injection approach employing on-line microwave reduction followed by hydride-generation quartz furnace atomic absorption spectrometry. Analyst (London) 1994 119 2785. (Dept. Environ. Sci. Univ. Plymouth Plymouth UK PL4 8AA). British Standards Institution Method for determination of sodium potassium calcium and magnesium contents of fruit and vegetable juices by atomic absorption spectrometry. British Standard BS EN 11341995 15 Jan 1995 1995 16. (389 Chiswick High Rd. London UK W4 4AL). Lopez Molinero A. Rubio C. Castillo J. R. Possibilities for graphic representation of multifactor simplex optimization. Anal. Chim. Acta 1994 297 417. (Dept. Anal. Chem.Fac. Sci. Zaragoza Univ. 50009 Zaragoza Spain). Barshick C. M. Shaw R. W. Young J. P. Ramsey J. M. Isotopic analysis of uranium using glow discharge optogalvanic spectroscopy and diode lasers. Anal. Chem. 1994,66,4154. (Chem. and Anal. Sci. Div. Oak Ridge Natl. Lab. Oak Ridge TN 37831-6375 UK). Bendicho C. Evaluation of an automated thermospray interface for coupling electrothermal atomization atomic absorption spectrometry and liquid chromatog- raphy. Anal. Chem. 1994 66,4375. (Dept. Quim. Anal. y Alim. Univ. Vigo 32004 Ourense Spain). Santosa S. J. Tanaka S. Inductively coupled plasma mass spectrometry for sequential determination of trace metals in rain and river waters using electrothermal vaporization. Anal. Lett. 1995 28 509. (Dept. Appl. Chem. Fac. Sci.and Technol. Keio Univ. Yokohama 223 Japan). Inokuma S. Hasegawa K. Sakai S. Nishimura J. Aminimide as an extractant for heavy- and transition metal cations. Chem. Lett. 1994 9 1729. (Dept. Chem. Gunma Univ. Kiryu 376 Japan). Maun A. R. Martinez Ada R. Salvador A. de la Guardia M. Speciation of calcium in ternary mixtures of calcium compounds by flame atomic absorption spectrometry and slurry atomization. Ciencia 1994 2 87. (Dept. Anal. Chem. Univ. Valencia 46100 Burjassot Valencia Spain). Carlosena A. Fernandez E. Prada D. Extraction of metals from olive leaves reference material with micro- wave assisted nitric acid-hydrogen peroxide digestion. Quim. Anal. (Barcelona) 1994 13 214. (Dept. Quim. Anal. Univ. La Coruna 15071 La Coruna Spain). Iwatsuki M. Sagawa K.Kitamura T. Fukasawa T. Determination of corundum spinel and aluminium nitride in slag on an aluminium-alloy melt by X-ray diffraction combined with selective dissolution. Bunseki Kagaku 1995 44 97. (Dept. Appl. Chem. and Biotechnol. Fac. Eng. Yamanashi Univ. Kofu Yamanashi 400 Japan). Sato K. Kohori M. Ide K. Hotta H. Okochi H. X-ray fluorescence analysis of submarine sediments by low-dilution fusion and matrix correction with use of theoretical alpha-coefficients. Bunseki Kagaku 1995,44 143. (Natl. Res. Inst. Metals Tsukuba Ibaraki 305 Japan). Christensen L. H. Ciceri G. Facchetti S. Duane M. Simple sample pretreatment methods in a mobile laboratory situation at a polluted industrial site. Quim. Anal. (Barcelona) 1994,13 S43. (Dept. Chem. Danish Technol. Inst. 2630 Taastrup Denmark).Fuwa K. My memory of spectroscopy in the USA an exciting era of atomic emission atomic absorption and atomic fluorescence. Spectrochim. Acta Part B 1994 49 1211. (Univ. Tokyo Musashino Tokyo 180 Japan). de Galan L. Survival in atomic spectrometry. Spectrochim. Acta Part B 1994 49 1221. (Unilever Res. Lab. Vlaardingen Netherlands).9513469 9513470 9513471 9513472 9513473 9513474 9513475 9513476 9513477 9513478 9513479 9513480 9513481 Pukhovskaya V. M. Grebneva 0. N. Maryutina T. A. Kuz’min N. M. Spivakov B. Ya. Inductively coupled plasma atomic emission spectroscopic determi- nation of rare earth elements in geological samples after preconcentration by countercurrent chromatogra- phy - Part 11. Spectrochim. Acta Part B 1995 50 5. (Vernadskii Inst.Geochem. and Anal. Chem. Russian Acad. Sci Moscow 117975 Russia). Battagliarin M. Sentimenti E. Scattolin R. Innovative sample-preparation procedure for trace and ultratrace analysis on non-conducting powders by direct current glow discharge mass spectrometry. Spectrochim. Acta Part B 1995 50 13. (Enirisorse Cerive 30175 Porto Marghera (VE) Italy). Schierle C. Thorne A. P. Inductively coupled plasma Fourier-transform spectrometry a study of element spectra and a table of inductively coupled plasma lines. Spectrochim. Acta Part B 1995 50 27. (Freiberger Elektronikwerkst. GmbH 09584 Freiberg Germany). Fey F. H. A. G. Benoy D. A. van Dongen M. E. H. van der Muller J. A. M. Model for the behaviour of analyte in the inner channel of an inductively coupled plasma.Spectrochirn. Acta Part B 1995 50 51. (Phys. Dept. Eindhoven Univ. Technol. 5600 MB Eindhoven Netherlands). Galley P. J. Homer J. A Hieftje G. M. Automated simplex optimization for monochromatic-imaging inductively coupled plasma atomic emission spec- troscopy. Spectrochim. Acta Part B 1995,50,87. (Dept. Chem. Indiana Univ. Bloomington IN 47405 USA). Eisert R. Levsen K. Wiinsch G. Element-selective detection of pesticides by gas chromatography-atomic emission detection and solid-phase micro-extraction. J. Chrornatogr. A 1994 683 175. (Dept. Anal. Chem. Fraunhofer Inst. Toxicol. and Aerosol Res. 30625 Hannover Germany). Sanz-Medel A. Aizpun B. Marchante J. M. Segovia E. Fernandez M. L. Blanco E. Vesicle-mediated high-performance liquid chromatography coupled to atomic detection for speciation of toxic elements.J. Chrornatogr. A 1994 683 233. (Dept. Phys. and Anal. Chem. Univ. Oviedo 33006 Oviedo Spain). Prokisch J. Kovacs B. Gyori Z. Loch J. Interfacing ion chromatography with inductively coupled plasma atomic emission spectrometry for the determination of chromium(II1) and chromium(v1). J. Chromatogr. A 1994 683 253. (Debrecen Agric. Univ. 4032 Debrecen Hungary). Schlegel D. Mattusch J. Dittrich K. Speciation of arsenic and selenium compounds by ion chromatogra- phy with inductively coupled plasma atomic emission spectrometry detection using the hydride technique. J. Chromatogr. A 1994 683 261. (Dept. Anal. Chem. Centre Environ. Res. 043 18 Leipzig Germany). Siles Cordero M. T. Garcia de Torres A. Can0 Pavon J. M.Bosch Ojeda C. Determination of cadmium in biological samples by inductively coupled plasma atomic emission spectrometry after extraction with 1,5-bis [ phenyl-( 2-pyridyl)methylene]-thiocarbonohyd- razide. Mikrochim. Acta 1994 116 173. (Dept. Anal. Chem. Fac. Sci. Univ. Malaga 29071 Malaga Spain). Janak K. Grimvall E. Ostman C. Colmsjo A. Gas chromatography-atomic emission detection (GC-AED) set up for bio-monitoring of PCBs and methylsulfonyl- PCBs. J. Microcolumn Sep. 1994 6 605. (Dept. Anal. Chem. Natl. Inst. Occup. Health 171 84 Solna Sweden). Petersson L. R. Determination of calcium magnesium and phosphorus in small amounts of rat tissues by direct current plasma (DCP) atomic emission spec- trometry. Anal. Lett. 1994 27 2471. (Dept. Chem. Natl. Vet. Inst.750 07 Uppsala Sweden). Hill C. M. Street K. W. Philipp W. H. Tanner S. P. Determination of copper in tap water using solid-phase 9513482 9513483 9513484 9513485 9513486 9513487 9513488 9513489 9513490 951349 1 9513492 9513493 9513494 9513495 9513496 spectrophotometry. Anal. Lett. 1994 27 2589. (Univ. Akron Akron OH 44325 USA). Tokalioglu S. Kartal S. Elci L. Determination of copper cadmium lead and bismuth in high-purity zinc metal samples by atomic absorption spectrometry after preconcentration using Amberlite XAD- 1180 resin. Anal. Sci. 1994 10 779. (Dept. Chem. Fac. Arts and Sci. Univ. Erciyes Kayseri Turkey). Shrader D. Multitasking atomic absorption spec- trometer. Am. Lab. (Fairfield Conn.) 1994 26( 1 l) 24C. (Varian Opt. Spectrosc. Instruments Wood Dale IL 60191 USA).Potter D. ICP-MS instrument for the modern labora- tory. Am. Lab. (Fairfield Conn.) 1994 26(11) 35. (Hewlett Packard Co. Wilmington DE 19808 USA). Devilliers D. Study of surfaces by tunnel-effect microscopy and atomic force microscopy. Analusis 1994 22 M8. (Lab. Electrochim. Univ. Pierre et Marie Curie 75252 Paris 05 France). Alegria A. Barbera R. Farre R. Moreno A. GFAAS determination of selenium in infant formulae using a microwave digestion method. Nahrung 1994 38 382. (Dept. Nutr. and Food Chem. Fac. Pharm. Univ. Valencia 46 100 Burjassot Valencia Spain). Bel’skii N. K. Timashuk E. L. Ochertyanova L. I. Garmash A. V. Determination of refractory carbide- forming elements zirconium hafnium and niobium by thermoelectrical atomic absorption spectroscopy.Zh. Anal. Khim. 1994 49 825. (Kurnakov Inst. Gen. and Inorg. Chem. Russian Acad. Sci. Moscow 117907 Russia). Stronkhorst J. Vos P. C. Misdorp R. Trace metals PCBs and PAHs in benthic (apipelic) diatoms from intertidal sediments; a pilot study. Bull. Enuiron. Contarn. Toxicol. 1994 52 818. (Natl. Inst. Mar. and Coastal Management 2500 EX The Hague Netherlands). Okoye C. 0. B. Lead and other metals in dried fish from Nigerian markets. Bull. Enuiron. Contam. Toxicol. 1994 52 825. (Dept. Pure and Ind. Chem. Univ. Nigeria Nsukka Nigeria). Anderson K. A. Isaacs B. Determination of antimony in environmental samples by hydride generation- inductively coupled plasma spectrometry. J. AOAC Int. 1994 77 1562. (Food Sci. and Toxicol. Dept. Coll. Agric. Univ. Idaho Moscow ID 83844-2203 USA).Martin A. M. Sanchez M. Espinosa P. Bagur G. Determination of tin in canned fruits and vegetables by atomic absorption spectrometry and liquid-liquid extraction. J. AOAC Znt. 1994 77 1627. (Dept. Anal. Chem. Fac. Sci. Unvi. Granada 18071 Granada Spain). Schaldach G. Berndt H. High-performance flow flame atomic absorption spectrometry for interference-free trace determination. Fresenius’ J. Anal. Chem. 1994 350,481. (Inst. Spektrochem. Angew. Spektrosk. 44139 Dortmund Germany). Figura P. Osae G. Determination of total chlorine in di-isocyanates by X-ray fluorescence spectroscopy. Am. Lab. (FairJeld Conn.) 1994 26 24K. ( O h Chem. Res. Cheshire CT 06410-0586 USA). Wang R.-j. Feng L.-y. Adaptation and application of a fundamental-parameters programme for X-ray fluo- rescence analysis to a microcomputer. Fenxi Huaxue 1994 22 1037.(Lab. Ore Deposit Geochem. Guiyang Inst. Geochem. Chinese Acad. Sci. Guiyang 550002 China). Shen K. Determination of trace aluminium in steel by a time-resolved method. Guangpuxue Yu Guangpu Fenxi 1994 14(3) 63. (Inst. Iron and Steel Wuhan Iron and Steel Corp. Wuhan 430080 China). Wu X.-d. He H.-j. Xue Y. Study on the determination of 18 mineral elements in vegetables by ICP-AES. Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 333R9513497 9513498 9513499 9513500 9513 50 1 9513502 9513503 9513504 9513505 9513506 9513507 9513508 9513509 95/3 5 10 334 R Guangpuxue Yu Guangpu Fenxi 1994,14( 3) 67. (Beijing Res. Centre Vegetables 10008 1 Beijing China). Chen HA.Du J.-x. Determination of trace amounts of arsenic in environmental samples by hydride generation atomic absorption spectrophotometry. Guangpuxue Yu Guangpu Fenxi 1994 14(3) 87. (Changchun Inst. Appl. Chem. Acad. Sin. Changchun 130022 China). Yuan Q.-h. Determination of mineral micro-elements in wild white stab fruit juice surface material by rich- oxygen-acetylene atomic absorption spectrophotome- try. Guangpuxue Yu Guangpu Fenxi 1994 14(3) 97. (Ningxia Anal. and Test Centre Yingchuan 750021 China). Zhang M.-y. Yuan L.-z. Tian J.-h. Determination of selenium in rice garlic bulbs and tea by flame AAS with a slotted quartz tube. Guangpuxue Yu Guangpu Fenxi 1994 14(3) 101. (Dept. Chem. Suzhou Univ. Suzhou 215006 China). Guo B.-b. Zhang C.-z. Determination of ultra-trace gold platinum rhodium and palladium by flameless AAS in geological samples after enrichment with minified fire assay through sulfide button.Yankuang Ceshi 1994 13(2) 92. (Xian Inst. Geol. and Miner. Resour. Xian 710054 China). Zhang P.-y. Peng H.-w. GFAAS determination of trace gallium and thallium in geological samples by introducing the sample as a suspension. Yankuang Ceshi 1994 13(2) 96. (Res. Inst. Geol. Miner. Resour. CNNC Guilin 541004 China). Zhang Y.-s. Determination of major minor and trace elements in zircon by ICP-AES. Yankuang Ceshi 1994 13(2) 121. (Inst. Miner. Resour. Xinjiang Urumqi 830000 China). Wang W.-m. Zhang M.-q. Determination of trace selenium and tellurium in geological samples by isobutyl methyl ketone extracton - graphite furnace atomic absorption spectrometry.Yankuang Ceshi 1994 13( 2) 125. (Lab. Geol. Bur. Qinghai Province Xining 810001 China). Chen Y.-j. Deng S.-w. Liang G.4. Non-destructive testing method for gold and silver ornaments. Yankuang Ceshi 1994 13(2) 145. (Inst. Rock and Miner. Anal. Min. Geol. and Miner. Resour. Beijing 100037 China). Guo W.-y. Zeng X.-j. ICP-AES determination of copper zinc cadmium manganese iron cobalt and lead in natural water after preconcentration of their PAN-chelates on foaming plastics. Lihua Jianyan Huaxue Fence 1994 30 289. (Jinzhou Med. Coll. Liaoning 121001 China). Liu S.-t. ICP-AES rapid determination of calcium in phytic acid. Lihua Jianyan Huaxue Fence 1994 30 302. (Guangxi Res. Centre Anal. and Tests Nanning 530022 China). Zhang J. Meng P.-x.Some problems in the flame AAS determination of chromium. Lihua Jianyan Huaxue Fence 1994 30 306. (Kunming Metallurgy Res. Inst. Yunnan 650031 China). Deng B. Gao Y.-g. Atomization mechanism of europium nitrate on a graphite probe surface in a graphite furnace. Fenxi Huaxue 1994 22 1002. (Dept. Chem. Qinghua Univ. Beijing 100084 China). Iwashita M. Ando H. Kageyama H. Shimamura T. Evaluation of the water quality of the Sagami River and its tributaries by ICP-MS. Bunseki Kagaku 1994 43 925. (Sch. Hyg. Sci. Kitazato Univ. Sagamihara Kanagawa 228 Japan). Shimizu T. Ohya K. Shijo Y. Graphite furnace AAS determination of mercury in water after preconcen- tration with one drop of solvent. Bunseki Kagaku 1994 43 971. (Dept. Appl. Chem. Fac. Eng. Utsunomiya Univ.Utsunomiya Tochigi 321 Japan). 951351 1 95/35 12 95/35 13 9513514 95/35 15 9513516 95/35 17 95/35 18 9513519 9513520 9513521 9513522 9 513 523 Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 Krekler S. Frenzil W. Schulze G. Simultaneous determination of iron(n)/iron(m) by sorbent extraction with flow-injection atomic absorption detection. Anal. Chim. Acta 1994 296 115. (Inst. Tech. Umweltschutz Tech. Univ. Berlin 10623 Berlin Germany). Townshend A. et al. Encyclopaedia of Analytical Science. Academic Press Inc. San Diego CA USA 1995. 0 12 226700 1. 6208 pp. Sneddon J. Advances in Atomic Spectroscopy. Vol. 2. JAI Press Ltd. London UK 1995. 1 55938 701 7. 300pp. Dedina J. Tsalev D. L. Hydride generation atomic absorption spectrometry. John Wiley and Sons Ltd.Chichester W. Sussex UK 1995.0 471 95364 4. 544 pp. Burguera J. L. Burguera M. Liquid sample introduc- tion devices in flow injection atomic spectroscopy. J. Anal. At. Spectrom. 1995 10 473. (IVAIQUIM Fac. Sci. Univ. Los Andes P.O. Box 542 Merida 5101-A Venezuela). Burguera J. L. Burguera M. Rivas C. Carrero P. Gallignani M. Brunetto M. R. On-line ion exchange for the removal of sulfur anion interference on the determination of manganese in geothermal fluids by flow injection electrothermal atomic absorption spec- trometry. J. Anal. At. Spectrom. 1995 10 479. (IVAIQUIM Fac. Sci. Univ. Los Andes P.O. Box 542 Merida 5101-A Venezuela). Alvarado J. Cristiano A. R. Curtius A. Fluoride as a chemical modifier for the determination of phosphorous by electrothermal atomic absorption spectrometry. J.Anal. At. Spectrom. 1995 10 483. (Dept. Quim. Univ. Simon Bolivar Aptd. Postal 89000 Caracas 1080-A Venezuela). Negretti de Bratter V. Bratter P. Reinicke A. Schulze G. Alvarez W. 0. L. Alvarez N. Determination of mineral and trace elements in total diet by inductively coupled plasma atomic emission spectrometry comparison of microwave-based digestion and pressurized-ashing systems using different acid mixtures. J. Anal. At. Spectrom. 1995 10 487. (Dept. Trace Elements in Health and Nutr. Hahn-Meitner Inst. Berlin Glienicker Str. 100 D-14109 Germany). Yang W.-m. Ni Z.-m. Atomization efficiencies of bismuth lead manganese chromium and gallium under stabilized temperature platform furnace conditions. J. Anal. At. Spectrom. 1995 10 493.(Res. Centre Eco- Environ. Sci. Acad. Sin. P.O. Box 2871 Beijing China). Arruda M. A. Z. Gallego M. Valcarcel M. Flow- through microwave digestion system for the determi- nation of aluminium in shellfish by electrothermal atomic absorption spectrometry. J. Anal. At. Spectrom. 1995 10 501. (Dept. Anal. Chem. Fac. Sci. Univ. Cordoba E-14004 Cordoba Spain). Lasztity A. Krushevska A. Kotrebai M. Barnes R. M. Amarasiriwardena D. Arsenic determination in environmental biological and food samples by induc- tively coupled plasma mass spectrometry. J. Anal. At. Spectrom. 1995 10 505. (Dept. Chem. Lederle Grad. Res. Centre Univ. Massachusetts Box 34510 MA Farinas J. C. Cabrera H. P. Larrea M. Improvement in the ion exchange chromatographic separation of rare earth elements in geological materials for their determi- nation by inductively coupled plasma atomic emission spectrometry. J.Anal. At. Spectrom. 1995 10 511. (Inst. Ceram. y Vidrio (CSIC) 28500 Arganda del Rey Madrid Spain). Holmberg A. Meurling L. Wernli B. Weinreich R. Analysis of boron in dextran-sulfhydrylborane conju- gates. Adv. Neutron Capture Ther. [Proc. Int. Symp.] 5th 2992 1993 435. (Kabi Pharm. Diagn. AB 75182 Uppsala Sweden). 01003-4510 USA).9-5/3524 9513525 9513526 9513527 9513528 9513529 9513530 9513531 95/3532 9513533 9513534 95/3535 9 513 5 3 6 De Gendt S. Van Grieken R. E. Ohorodnik S. K. Hamson W. W. Parameter evaluation for the analysis of oxide-based samples with radiofrequency glow dis- charge mass spectrometry. Anal. Chem. 1995 67 1026.(Dept. Chem. Univ. Antwerp B-2610 Antwerp Belgium). Hidaka H. Ebihara M. Shima M. Determination of the isotopic compositions of samarium and gadolinium by thermal ionization mass spectrometry. Anal. Chem. 1995 67 1437. (Dept. Chem. Tokyo Metropolitan Univ. Hachioji 192-03 Japan). Beauchemin D. On-line standard additions method with ICP-MS using flow injection. Anal. Chem. 1995 67 1553. (Dept. Chem. Queen’s Univ. Kingston Ontario Canada K7L 3N6). Yoshinaga J. Shirasaki T. Oishi K. Morita M. Isotope dilution analysis of selenium in biological materials by nitrogen microwave-induced plasma mass spectrometry. Anal. Chem. 1995 67 1568. (Natl. Inst. Environ. Studies Tsukuba 305 Japan). Martin-Esteban A. Fernandez P. Perez-Conde C. Gutierrez A. Camara C. On-line preconcentration of aluminium with immobilized chromotrope 2B for the determination by flame atomic absorption spectrometry and inductively coupled plasma mass spectrometry.Anal. Chim. Acta 1995 304 121. (Dept. Quim. Anal. Fac. Cien. Quim. de la Univ. Complutense 28040 Madrid Spain). Higashiura M. Uchida H. Uchida T. Wada H. Inductively coupled plasma mass spectrometric determi- nation of gold in serum comparison with flame and furnace atomic absorption spectrometry. Anal. Chim. Acta 1995 304 317. (Diag. Sci. Dept. Shionogi Biomedical Lab. Shionogi Co. Ltd. Mishima Settsu Osaka 566 Japan). Nishio Y. Tsutsumi M. Gamo T. Sano Y. Hydrogen effect of the 6I3C value of CO measured by mass spectrometry with electron-impact ionization. Anal. Sci. 1995 11 9. (Dept. Earth Plant Sci.Hiroshima Univ. Higashi-Hiroshima 724 Japan). Fukuda M. Hayashibe Y. Sayama Y. Determination of nickel cobalt copper thorium and uranium in high- purity zinc metal by ICP-MS with on-line matrix separation. Anal. Sci. 1995 11 13. (Central Res. Inst. Mitsubishi Mater. Co. Omiya 330 Japan). Toda E. Hioki A. Determination of impurities in high- purity selenium by inductively coupled plasma mass spectrometry after matrix separation with thiourea. Anal. Sci. 1995 11 115. (Central Res. Lab. Sumitomo Met. Min. Co. Ltd. Chiba 272 Japan). Sahoo S. K. Masuda A. Simultaneous measurement of lithium and boron isotopes as lithium tetraborate ion by thermal ionization mass spectrometry. Analyst (Cambridge UK) 1995 120 335. (Dept. Chem. Univ. Electro-Communications Tokyo 182 Japan).High K. A. Blais J.-S. Methven B. A. J. McLaren J. W. Probing the characteristics of metal-binding proteins using high-performance liquid chromatography atomic absorption spectroscopy and inductively coupled plasma mass spectrometry Analyst (Cambridge UK) 1995 120 629. (Dept. Food Sci. Agric. Chem. McGill Univ. Ste. Anne de Bellevue PQ Canada H9X 3V9). Arslan F. Behrendt M. Ernst W. Finckh E. Greb G. Gumbmann F. Haller M. Hofmann S. Karschnick R. et al. Trace analysis of the radionuclides 90Sr and 89Sr in environmental samples. 11 accelerator mass spectrometry (AMS). Angew. Chem. Int. Ed. Engl. 1995 34 183. (Phys. Inst. Univ. Erlangen-Nuernberg D-91058 Erlangen Germany). Hess K. R. Barshick C. M. Duckworth D. C. Smith D. H. Influence of solution-deposited discharge relative ion yields.Appl. Spectrosc. 1994 48 1307. (Dept. Chem. Franklin Marshall Coll. Lancaster PA 17604 USA). 9513537 9513538 9513 539 9513540 9 513 54 1 9513542 9513543 9513544 9513545 9513546 9513547 9 513 548 9513549 9513550 9513551 Myers D. P. Heintz M. J. Mahoney P. P. Li G. Heiftje G. M. Characterization of a radiofrequency glow dischargeltime-of-flight mass spectrometer. Appl. Spectrosc. 1994 48 1337. (Dept. Chem. Indiana Univ. Bloomington IN 47405 USA). Vollkopf U. Barnes K. Rapid multi-element analysis of urine. At. Spectrosc. 1995 16 19. (Bodenseewerk Perkin-Elmer GmbH D-88647 Uberlingen Germany). Frank F. Glaser W. Schiffers A. Determination of trace elements in electrolfilter ashes from brown coal-fired boilers in the Rhenisch region in Germany. Braunkohle Bergbautech.1994 46 31. ( Kraftwerk Goldenbergwerk Rheinisch-Westfael. Elektrizitaetswerke Energ. A.-G. D-50344 Huerth Germany). Luten J. B. Muys Th. van Dokkum W. Determination of stable isotope ratio of zinc copper iron in faeces and calcium in urine by ICP-MS. Ber. Bundesforschungsanst. Ernaehr. BFE-R-93-01 Pt. 2 1993 161. (TNO Nutrition Food Res. 3700 AJ Zeist Netherlands). Owen L. M. W. Crews H. M. Bishop N. J. Massey R. C. Study of copper zinc and aluminium in the gut content of guinea pigs using size exclusion chromatogra- phy-inductively coupled plasma mass spectrometry. Ber. Bundesforschungsanst. Ernaehr. BFE-R-93-01 Pt. 1 1993,284-8. (Dunn Nutr. Unit Medical Res. Council Cambridge UK CB4 1XJ). Hall G. E. M. Vaive J. E. McConnell J.W. Development and application of a sensitive and rapid analytical method to determine the rare-earth elements in surface waters. Chem. Geol. 1995 120 91. (Geol. Surv. Canada 601 Booth St. Ottawa Ontario Canada K1A OE8). Marty B. Lenoble M. Vassard N. Nitrogen helium and argon in basalt a static mass spectrometry study. Chem. Geol. 1995 120 183. (URA 736 CNRS Lab. MAGIE Univ. Pierre et Marie Curie 4 Place Jussieu F-75252 Paris 05 France). Vaglio G. A. Mass spectrometric methods in inorganic chemistry. Chim. Ind. (Milan) 1993 75 8. (Dipt. Chim. Org. Appl. Univ. Torino Italy). Zhang Q.-l. Zhao D.-m. Atomic weight of samarium. Chin. Sci. Bull. 1994 39 1265. (Inst. Geol. Chinese Acad. Geol. Sci. Beijing 100037 China). Luke A. H. Isotope ratio mass spectrometry in nutrition research. Diss.Abstr. Int. By 1994 55 1812. (Univ. Chicago Chicago IL USA). Van Straaten M. Analytical glow discharge mass spectrometry physical aspects and applications. Diss. Abstr. Int. B 1994 55 2192. (Univ. Instelling Antwerpen Belgium). Vanderpool R. A. Hoff D. Johnson P. E. Use of inductively coupled plasma mass spectrometry in boron-10 stable isotope experiments with plants rats and humans. Environ. Health Perspect. 1994 102( 7) 13. (Agric. Res. Serv. US Dept. Agric. Grand Forks ND USA). Wang Z.-d. Liu Z.-y. Hou J.-q. Yao Y.-y. Zhang L.-h. Luo Y.-y. Accuracy in the determination of 15N natural abundance. Fenxi Shiyanshi 1994 13(4) 74. (Chinese Acad. Agric. Sci. Beijing 100081 China). Hub W. Amphlett H. Application of ETV-ICP-MS in semiconductor process control.Fresenius’ J. Anal. Chem. 1994 350 587. (Siemens AG D-81739 Munich Germany). Jochum K. P. Laue H.-J. Seufert H. M. Hofmann A. W. First analytical results using a multi-ion counting system of a spark source mass spectrometer. Fresenius’ J. Anal. Chem. 1994 350 642. (Max-Planck-Inst. Chem. D-55020 Mainz Germany). Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 335 R9 513 5 52 9513553 9513554 9513555 9513556 9 513 5 57 9513558 9513 5 59 9513560 9 513 56 1 9 513 562 9513563 9513564 9513565 9513566 336 R Henrion A. Reduction of systematic errors in quantitat- ive analysis by isotope dilution mass spectrometry (IDMS) an iterative method. Fresenius' J. Anal. Chem. 1994 350 657. (Phys.-Tech. Bundesanstalt D-38116 Braunschweig Germany).Lieser K. H. Fey W. Isotopic fingerprint method assessment of the origin of rare earth compounds from the isotope ratios of lead impurities. Fresenius' J. Anal. Chem. 1995 351 129. (Tech. Hochsch. Eduard Zintl- Inst. D-64289 Darmstadt Germany). Pilger C. Leis F. Tschopel P. Broekaert J. A. C. Tolg G. Analysis of silicon carbide powders with ICP-MS subsequent to sample dissolution without and with matrix removal. Fresenius' J. Anal. Chem. 1995 351 110. (Inst. Spektrochem. Angew. Spektrosk. D-44013 Dortmund Germany). Deng Z.-g. Guo D.-s. Measurement of the isotope ratios and concentrations of zinc by thermal ionization mass spectrometry using double isotope dilution. He Huaxue Yu Fangshe Huaxue 1994,16 142. (China Inst. At. Energy Beijing 102413 China). Nakamura T.Measurements of environmental radio- nuclides with accelerator mass spectrometry. Hoshasen 1993 20 65. (Dating and Mater. Res. Centre Nagoya Univ. Chikusa Japan). Gomez Coedo A. Dorado Lopez T. Characteristics of flow injection inductively coupled plasma mass spec- trometry for boron analysis in steels. ISIJ Int. 1994 34 997. (Central Nac. Invest. Metal. Madrid 28040 Spain). Delmore J. E. Appelhans A. D. Olson J. E. Self imaging of surface ionization ion sources - where do the ions come from? Int. J. Mass Spectrom. Ion Processes 1994,140 11 1. (Idaho Natl. Eng. Lab. Idaho Falls Idaho USA). Gladyszewski L Thermoemission of Ce' ions and its fluctuations. Int. J. Mass Spectrom. Ion Processes 1994 140 123. (Inst. Phys. Maria Curie-Sklodowska Univ. 20-03 1 Lublin Poland).Aggarwal S. K. Jain H. C. Polyatomic ions in thermal ionization mass spectrometry - challenges and oppor- tunities. Int. J. Mass Spectrom. Ion Processes 1995 141 149. (Fuel Chem. Div. Bhabha At. Res. Centre Trombay Bombay 400 India). Blake E. Raynor M. W. Cornell D. On-line capillary supercritical fluid chromatography-inductively coupled plasma mass spectrometry for the analysis of organome- tallic compounds. J. High Resolut. Chromatogr. 1995 18 33. (Dept. Chem. Appl. Chem. Univ. Natal Durban 4001 South Africa). Meier-Augenstein W. On-line recording of 13C/12C ratios and mass spectra in one gas chromatographic analysis. J. High Resolut. Chromatogr. 1995 18 28. (Stable Isotope and GC-MS Lab. Univ. Children's Clinic D-69120 Heidelberg Germany). Kohler M.Schlunegger U. P. Tunable degree of fragmentation of volatile organic compounds with a low-pressure Penning ion source. J. Mass Spectrom. 1995 30 134. (Inst. Org. Chem. Univ. Bern CH-3012 Bern Switzerland). Uchida H. Sakao S. Suzuki T. Sample introduction in inductively coupled plasma mass spectrometry using an ultrasonic nebulization system. Kenkyu Hokoku- Kanagawa-ken Kogyo Shikensho 1994 65 38. (Ind. Res. Inst. Kanagawa Prefect. Yokohama 236 Japan). Koelbl G. Concepts for the identification and determi- nation of selenium compounds in the aquatic environ- ment. Mar. Chem. 1995 48 185. (Inst. Anal. Chem. Karl-Franzens Univ. Graz Universitaetsplatz 1 A-8010 Graz Austria). Liu J.-l. Tong Y.-d. Zhang X.-q. Determination of trace rare earth impurities in high purity yttrium oxide 9513567 9513 5 68 9513569 9 513 5 70 951357 1 9 513 5 72 9513573 9513574 9513575 9513576 9513577 9513578 9513579 9513 5 80 Journal of Analytical Atomic Spectrometry November 1995 Vol.10 by ICP-MS. Zhongguo Xitu Xuebao 1994 12 68. (Jaingxi Prov. Anal. Testing Centre Nanchang China). Dubinin A. V. Baturin G. N. Rare earth elements in standard deep-sea iron-manganese ores and red clay. Okeanologiya (Moscow) 1994 34 228. (Inst. Okeanol. im. P.P. Shirshova Moscow Russia). Hall P. B. Stoddart D. Bjoroey M. Larter L. S. Brasher J. E. Detection of petroleum heterogeneity in Eldfisk and satellite fields using thermal extraction pyrolysis-GC GC-MS and isotope techniques. Org. Geochem. 1994 22 383. (Geolab Nor A/S N-7002 Trondheim Norway). Hoffmann E. Determination of trace elements in annual rings of trees by laser-ICP-MS. Nachr.Chem. Tech. Lab. 1994 42 886. (Berlin Germany). Henning W. 205Pb detection AMS and alternatives. Neues Jahrb. Mineral Abh. 1994,167,271. (Gesellschaft Schwerionenforschung GSI 6429 1 Darmstadt Germany). de Angelis G. Farnea E. Gadea A. Sferrazza M. Ackermann D. Bazzacco D. Bednarczyk P. Bizzeti P. G. Bizzeti Sona A. M. et al. Towards loOSn with GASP + Si-ball + recoil mass spectrometer high-spin states of "'Sn and lo31n. Nucl. Phys. A 1995 583 231. (INFN Lab. Naz. Legarno Legarno (Padova) Italy). Cherekdjian S. Ramsbey M. Anjum M. Trace elemental analysis of tungsten. Nucl. Instrum. Methods Phys. Res. Sect. B 1995 96 87. (Implant Center 643 River Oaks Parkway San Jose CA 95134 USA). Tourneaux C.Peltier G. Effect of water deficit on photosynthetic oxygen exchange measured using I8O2 and mass spectrometry in Solanum tuberosum L. leaf discs. Planta 1995 195 570. (Dept. Physiol. Vegetale et Ecosystemes CEA 13 108 St. Paul-lez-Durance France). Hener U. Faulhaber S. Kreis P. Mosandl A. Evaluation of authenticity of balm oil (Melissa officinalis L.). Pharmazie 1995 50 60. (Inst. Lebensmittelchem. Johann Wolfgang Goethe Univ. FrankfurtIMain Germany). Hall G. S. Scholtz H. Determination of stable lead isotopes in sequentially obtained tap water samples by inductively coupled plasma mass spectrometry. Proc.- Annu. Cong. Am. Water Works Assoc. 1994,819. (Dept. Chem. State Univ. New Jersey New Brunswick NJ 08903 USA). Valkiers S. de Bievre P. Near-absolute gas (isotope) mass spectrometry isotope abundance (and atomic weight) determination of boron and carbon.Process Technol. Proc. 1994 11 959. (Inst. Ref. Mater. and Measur. Comm. Eur. Commim.-JRC B-2440 Geel Belgium). Kinard W. F. Bibler N. E. Coleman C. J. Wyrick S. B. Inductively coupled plasma mass spectrometry studies of the chemistry of fission products and actinides in high-level wastes lessons that can be applied to environmental measurements. Radiochim. Acta 1994 66 259. (Dept. Chem. Coll. Charleston Charleston SC 29424 USA). Naraoka H. Ishiwatari R. Determination of stable carbon isotopic compositions of specific organic com- pounds and its applications to the geochemistry. Radioisotopes 1994 43 729. (Fac. Sci. Tokyo Metropolitan Univ. Hachioji 192-03 Japan).Breas O. Reniero F. Serrini G. Isotope ratio mass spectrometry analysis of wines from different European countries. Rapid Commun. Mass Spectrom. 1994 8,967. (Jt. Res. Centre Environ. Inst. 1-21020 Ispra Italy). Katayama I. Wada M. Tanaka J. Kawakami H. Schuessler H. A. Okada H. Nakamura T. Ohtani S. Becker O. et al. Ion trap-laser experiment at the INS cyclotron. Univ. Tokyo Inst. Nucl. Study INS-9513581 9513582 9513583 95/35 84 9513585 9513 5 86 9513587 9513588 9513 5 89 9513590 9513591 9513592 9513593 9513594 Rep. INS-Rep.-1066 1994 6. (INS Univ. Tokyo Tanashi 188 Japan). Nonose N. Kubota M. Effect of secondary discharge on spectroscopic and non-spectroscopic interferences in inductively coupled plasma mass spectrometry. Symp. Plasma Sci. Mater. 1994,7th 7.(Natl. Inst. Mater. and Chem. Res. Tsukuba 305 Japan). Shao M. Tang X.-y. Application of accelerator mass spectrometry in the research of atmospheric methane. Tongweisu 1994 7 187. (Centre Environ. Sci. Peking Univ. Beijing 100871 China). Kang J. S. Kim H. J. Determination of trace elements in organic tissues of rat by inductively coupled plasma mass spectrometry. Yakhak Hoechi 1993 37 57780. (Coll. Pharm. Chungnam Natl. Univ. Taejon 305-764 South Korea). Guo Z.-y. Yan S.q. Xiao M. Zhang Z.-f. Yang F.-l. Chen C.-e. Liu K.-x. Lu X.-y. Li B. et al. Injection system for AMS at Peking University. Yuanzineng Kexue Jishu 1994 28 390. (Inst. Heavy Ion Phys. Peking Univ. Beijing 10087 China). Zeng H.-f. Zhou S.-j. Determination of tungsten molybdenum and tin in geochemical samples by TRPO- cellulose extraction chromatographic preconcentration and ICP-MS.Yunkuang Ceshi 1994 13 259. (Inst. Rock and Miner. Anal. Minist. Geol. and Miner. Resour. Beijing 100037 China). Villa-Aleman E. Analysis of hydrogen isotope mixtures. U.S. Pat. Appl. US 933,145 01 Feb 1995 Appl. 21 Aug 1992; 17 pp. (US Dept. Energy USA). Shimada R. Okino A. Nomura J. Ishizuka H. Plasma torch for ICP mass spectrometric and atomic emission spectrometric analysis. Jpn. Kokai Tokkyo Koho JP 06,342,697 [94,342,697] (cl. H05H1/28) 13 Dec 1994 Appl. 931130,527 01 Jun 1993; 5pp. (Yokogawa Electric Corp. Japan). Naka H. Trace metal determination in acidic solutions by ICP mass spectrometry. Jpn. Kokai Tokkyo Koho JP 07 21,973 [95 21,9731 (Cl. HOlJ49/04) 24 Jan 1995 Appl.931164,560 02 Jul 1993; 5 pp. (Sumitomo Metal Ind. Japan). Ohgi T. Morita Y. Namikawa T. Yamazaki Y. Two-dimensional distributions of 0- and OH3- SIMS counts for SrCe,~,,Yb,~,,O proton conductor. Denki Kagaku Oyobi Kogyo Butsuri Kagaku 1994 62 886. (Dept. Electron. Chem. Tokyo Inst. Technol. Yokohama 227 Japan). Grebner Th. L. Neusser H. J. Laser produced ions stored in a cylindrical ion trap and detected in a reflectron time-of-flight mass spectrometer. Int. J. Mass Spectrom. Ion Processes 1994 137 L1. (Inst. Phys. und Theor. Chem. Tech. Univ. Munchen Lichtenbergstr. 4 Garching Germany). Pinto G. R. Stika K. M. Lloyd K. G. Elucidating ablation mechanisms through SIMS studies of cross- linked polymer surfaces. J. Phys. Chem. 1995 99 1543. (DuPont Imaging Systems and DuPont Corp.Centre Anal. Sci. Wilmington DE 19880 USA). Barckhaus R. H. Schmidt P. F. Hoelling H. J. Localization of lead in histological sections by elec- tronprobe X-ray microanalysis (EDAX) and laser microprobe mass analysis (LAMMA). An investigation of intracellular lead accumulation. Main Group Met. Chem. 1994 17 333. (Inst. Med. Phys. and Biophys. Univ. Munster D-48149 Munster Germany). Bedilov M. R. Aripov E. A. Khaitbaev K. Platinum ions in the multicomponent laser plasma. Uzb. Fiz. Zh. 1993 4 40. (Tashk. GU Tashkent Uzbekistan). Saastamoinen S. Likonen J. Neimo L. Paulapuro H. Steinus P. SIMS study of the adsorption of calcium and aluminium on unbleached and hydrogen peroxide bleached pressurized groundwood. Pap. Puu 1994 76 74. (Finland).9513595 9513596 9513597 9513598 9513599 9513600 9513601 9513602 9513603 9513604 9513605 9513 606 9513607 9513608 Gea L. Jauneau A. Vian B. Preliminary SIMS imaging of calcium distribution of ectomycorrhizas of Pinus pinaster and Hebeloma cylindrosporum. J. Trace Microprobe Tech. 1994 12 323. (Lab. Pathol. Veg. INA P-G Lab. Echanges Cell. 76134 Mont St. Aignan Cedex France). Swanson L. W. Lindquist J. M. Jaehnig M. C. Puretz J. Secondary ion mass spectrometry system. U.S. US 5,376,791 (Cl. 250-309; HOlJ37/28) 27 Dec 1994 US Appl. 685,844 15 Apr 1991; 8 pp. (FEI Co. ). Grasserbauer M. Friedbacher G. Hutter H. Leisch M. Imaging analytical chemistry trends in imaging and image processing for micro nano and surface analysis. Spec. Publ.-R. SOC. Chem. 1994 154 168. (Inst.Anal. Chem. Tech. Univ. Wien A-1060 Vienna Austria). De Bievre P. Valkiers S. Schaefer F. Peiser H. S. Seyfried P. High-accuracy isotope abundance measure- ments for metrology. PTB-Mitt. 1994 104 225. (Inst. Ref. Mater. Measure. B-2440 Geel Belgium). Kumpulainen H. Determination of natural uranium- series isotope ratios by mass spectrometry. VTT Tied. 1993 1503 17. (Reaktorilaboratorio Valtion Teknillinen Tutkimuskeskus Espoo Finland). Inoue Y. Kawabata K. Takahashi H. Endo G. Determination of inorganic and organic arsenic com- pounds in urine using ion chromatography with ICP-MS. Bunseki Kagaku 1995 44 203. (R & D Div. Yokogawa Anal. Syst. Inc. Musashino 180 Japan). Tsumura A. Okamoto R. Takaku Y. Yamasaki S. Direct determination of uranium in rainwater by high resolution ICP-MS with an ultrasonic nebulizer.Radioisotopes 1995 44 85. (Natl. Inst. Agro-Environ. Sci. Tsukuba 305 Japan). Caroli S.,Torre F. La Petrucci F. Violante N. On- line speciation of arsenical compounds in fish and mussel extracts by HPLC-ICP-MS. Enuiron. Sci. Pollut. Res. Int. 1994 1 205. (1st. Sup. di Sanita 1-00161 Rome Italy). High K. A. Methven B. A. McLaren J. W. Siu K. W. M. Wang J. Klaverkamp J. F. Blais J. S. Physico-chemical characterization of metal-binding proteins using HPLC-ICP-MS HPLC-MA-AAS and electrospray-MS. Fresenius’ J. Anal. Chem. 1995 351 393. (Dept. Food Sci. Agric. Chem. McGill Univ. Quebec Canada H9X 3V9). Thomas P. Sniatecki K. Inductively coupled plasma mass spectrometry application to the determination of arsenic species.Fresenius’ J. Anal. Chem. 1995 351 410. (Serv. Eaux-Environ. Inst. Pasteur Lille F-59019 Lille France). Freeman C. G. Herrick D. M. Bryan D. C. Kurz K. L. Mathews D. H. Perera P. A. A. Wolfs F. L. H. Zanni M. T. New focal plane detector system for the Rochester recoil mass spectrometer. Nucl. Instrum. Methods Phys. Res. Sect. A 1995 357 450. (Nucl. Struct. Res. Lab. Univ. Rochester Rochester NY 14627 USA). Engelmann U. Vassallo G. Analytical glove-box in the tritium magazine of ETHEL. Fusion Eng. Des. 1995 28 324. (Joint Res. Centre Eur. Comm. Safety Technol. Inst. Ispra Site 1-21020 Ispra (VA) Italy). Inagaki Y. Furuya H. Idemitsu K. Corrosion behav- iour of high-level nuclear waste glass under anoxic conditions. Measurement of elements with low solubility by ICP-MS.Kyushu Daigaku Chuo Bunseki Senta Hokoku 1994 12 18. (Fac. Eng. Kyushu Univ. Fukuoka 812-81 Japan). Goossens J. Moens L. Dams R. Inductively coupled plasma mass spectrometric determination of heavy metals in soil and sludge candidate reference materials. Anal. Chim. Acta 1995 304 307. (Inst. Nucl. Sci. Lab. Anal. Chem. Ghent Univ. Proeftuinstraat 86 9000 Ghent Belgium). Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 337 R9513609 9513 6 10 951361 1 95/36 12 95/36 13 9513614 9513615 95/36 16 9 5/36 17 9513618 95/36 19 9513620 951362 1 9 513 622 95/3623 338R Naraoka H. Yamada K. Ishiwatari R. Stable carbon isotope measurement of individual fatty acids using gas chromatography/isotope ratio monitoring mass spec- trometry (GCIIRMS). J.Mass Spectrom. SOC. Jpn. 1994 42 315. (Fac. Sci. Tokyo Metropolitan Univ. Hachioji 193-02 Japan). Ding H. Wang J.-s. Dorsey J. G. Caruso J. A. Arsenic speciation by micellar liquid chromatography with inductively coupled plasma mass spectrometric detection. J. Chromatogr. A 1995 694 425. (Dept. Chem. Univ. Cincinnati Cincinnati OH 45221-0172 USA). Bader K. P. Roeben A. Mass spectrometric detection and analysis of nitrogen fixation in Oscillatoria chalybea. Z. Naturjiorsch. C Biosci. 1995 50 199. (Fac. Biol. Univ. Bielefeld D-33501 Bielefeld Germany). Erlandson R. E. Boies M. T. Uy 0. M. Grebowsky J. M. MSX ion mass spectrometer measurement of contaminant and ambient ions. Proc. SPIE-Int. SOC. Opt. Eng. 1994 2261 181. (Appl. Phys. Lab. John Hopkins Univ. Laurel MD 20723 USA).Suzuki K. T. Itoh M. Ohmichi M. Detection of selenium-containing biological constituents by high- performance liquid chromatography-plasma source mass spectrometry. J. Chromatogr. B Biomed. Appl. 1995 666 13. (Fac. Pharm. Sci. Chiba Univ. 1-33 Yayoi Inage Chiba 263 Japan). Merritt D. A. Hayes J. M. Des Marais D. J. Carbon isotopic analysis of atmospheric methane by isotope- ratio-monitoring gas chromatography-mass spec- trometry. J. Geophys. Res. [Atmos.] 1995 100 1317. (Dept. Chem. Indiana Univ. Bloomington IN USA). Freeman J. H. Surface ionization ion sources. Brit. UK Pat. Appl. GB 2,278,952 (Cl. HOlJ27/26) 14 Dec 1994 Appl. 93112,159 12 Jun 1993; 6 pp. Zhou Q.-w. Zhao C.-h. Determination of trace arsenic in highly pure germanium oxide by hydride generation atomic absorption spectrometry.Fenxi Shiyanshi 1995 14 59. (Beijing Gen. Res. Inst. Non-Ferrous Metals Beijing 100088 China). Li B. Yin M. Determination of 14 rare earth impurities in high-purity lutetium oxide by ICP-MS. Fenxi Shiyanshi 1994 13 17. (Inst. Rock Miner. Anal. Min. Geol. and Miner. Resour. Beijing 100037 China). Li X.4 Zhou PA. Zheng Y.-m. Yang CA Wang X.-r. Determination of arsenic and antimony in tra- ditional Chinese medicine by hydride generation atomic absorption spectrometry. Fenxi Shiyanshi 1995 14 11. (Xiamen Traditional Chinese Med. Factory Xiamen China). Wang W.-q. Wei J-.z. Determination of K and Na in super-purity reagent with GFAAS. Guangpuxue Yu Guangpu Fenxi 1995 15 71. (46th Res. Inst. of Mach. and Elect. Ind. 300192 Tianjin China).Yuan Z.-n. Study of interfering mechanisms of per- chloric acid and salt with indium in GFAA using molecular absorption spectroscopy. Guangpuxue Yu Guangpu Fenxi 1995 15 89. (Hunan Imp. and Exp. Commodity Bureau 410007 Changsha China). Sun X. Determination of trace cadmium by FAAS with SrCo as a precipitant for preconcentration. Guangpuxue Yu Guangpu Fenxi 1995,15,97. (Oncology Lab. First Affiliated Hosp. Anhui Med. Univ. 230022 Hefei China). Li C.-q. Yuan X. Determination of 24 metallic elements in air of enclosed compartment by AAS. Guangpuxue Yu Guangpu Fenxi 1995 15 87. (718 Res. Inst. of CSSC 056027 Handan China). Piao Z.-x. Yang J.-f. Zeng X.-j. Chen X.-h. Correction of background interferences with Kalman filtering. Guangpuxue Yu Guangpu Fenxi 1995 15 61.(Changchun Inst. Appl. Chem. Acad. Sin. 130022 Changchun China). 9513624 9513625 9513626 9513627 9513628 9513629 9 513 630 9513631 9513632 9513633 9513634 9513635 9 5/363 6 9 513 6 3 7 Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 Zhang X.-h. Li H.-f. Yang Y.-f. Determination of minor components and impurities in platinum catalytic net by ICP-AES. Guangpuxue Yu Guangpu Fenxi 1995 15 41. (Kunming Inst. Precious Metals 650221 Kunming China) Zhang H. Yang Y.-y. Huang J.-f. Determination of rare earth elements by the method of interference coefficient repeated correction with ICP-AES. Guangpuxue Yu Guangpu Fenxi 1995 15 49. (Inst. Mod. Appl. Chem. Nanchang Univ. 330047 Nanchang China). Lin S.4 Lu C.-g. Tong Z.-y. Chiu H. Comparison of the analytical performance between membrane and U-tube phase separators for flow injection hydride generation atomic fluorescence spectrometry.Guangpuxue Yu Guangpu Fenxi 1995 15 69. (Dept. Appl. Chem. China Univ. Geosci. 430074 Wuhan China). Wang J.-d. Tian L.-q. Wang L.-s. Application of atomic absorption spectrometry for organic analysis (111) - determination of tannins in tea. Gaodeng Xuexiao Huaxue Xuebao 1995 16 536. (Dept. Chem. Xinjiang Univ. Urumqi 830046 China). Qin Y.-c. Jiang Z-c. Hu B. Zeng Y. Direct determination of boron in botanical samples by fluorination electrothermal vaporization-inductively coupled plasma atomic emission spectrometry. Fenxi Huaxue 1995 23 60. (Dept. Chem. Wuhan Univ. Wuhan 430072 China). Zhang Y.4. Determination of trace strontium in natural mineral water by flow injection flame atomic absorption spectrometry.Fenxi Huaxue 1995 23 180. (Res. Inst. Qilu Petrochem. Corp. Zibo 255400 China). He H.-k. Xie Y.-s. Chen J.-h. Fang H.-q. Studies on the spectral line profiles in Zeeman effect atomic absorption spectroscopy. I. Overlapping relationship for calculated line profiles for AE AA and ZAA. Huaxue Xuebao 1995 53 57. (Chinese Natl. Anal. Centre Guangzhou 510070 China). He H.-k. Xie Y.-s. Chen J.-h. Fang H.-q. Studies on the spectral line profiles in Zeeman effect atomic absorption spectroscopy. 11. Investigation of the R value in ZAAS. Huaxue Xuebao 1995 53 68. (Chinese Natl. Anal. Centre Guangzhou 510070 China). Yao J.-y. Xie W.-b. Hu QJ. Lian C.-z. Direct determination of silicon in high temperature alloy by graphite furnace atomic absorption spectrometry.Fenxi Huaxue 1995 23 284. (Changchun Inst. Appl. Chem. Chinese Acad. Sci. Changchun 130022 China). An D.-y. Gong W.-s. Determination of trace arsenic in drinking water by hydride gheneration-ICP emission spectrometry. Fenxi Ceshi Xuebao 1995 14 42. (Exp. Centre South China Normal Univ. Guangzhou 510631 China). Yang X.-t. He H.-k. Theoretical method of calculation of the absorbance in ZAAS method of the constant and transverse magnetic field. Fenxi Ceshi Xuebao 1995 14 20. (Inst. Rock and Miner. Anal. Miner. Geol. and Miner. Resour. Beijing 100037 China). Chen H.-w. Zhu R.-c. Mao X.-q. Atomic absorption spectrometric determination of arsenic in steel and geological samples using hydride generation combined with slotted tube atom-trap technique. Fenxi Ceshi Xuebao 1995 14 66.(Dept. Chem. Hangzhou Univ. Hangzhou 310028 China). Zhang X.-h. Chen X.-k. Hung Z.-r. Cai S.-w. Study of the correlation between the effect of inorganic acid and the intensity of band of OH in ICP-AES. Anal. Sci. 1994 10 25. (Dept. Chem. Naukai Univ. Tianjin 300071 China). Peng L.-q. Yao J.-y. HC-GF in situ preconcentration AAS determination of tellurium in nickel-base alloys. Lihua Jianyan Huaxue Fence 1995,31,75. (Changchun9513638 9513639 9 513 640 95/364 1 9513642 9513643 9513644 9513645 9513646 9513647 9513648 9-5/3649 9513650 9513651 Inst. Appl. Chem. Chinese Acad. Sci. Changchun 130022 China). Cai HA. Zhang B.-c. Zhou L.-q. AAS determination of traces on indium in human hair with graphite probe furnace.Lihua Jianyan Huaxue Fence 1995 31 21. (Dept. Chem. Hubei Univ. Wuhan 430062 China). Weng Y.-h. Flame atomic absorption spectrometry. Faming Zhuanli Shenqing Gongkai Shuomingshu CN 1,076,278 (Cl. GOlN21/31) 15 Sep 1993 Appl. 92,101,560 09 Mar 1992; 11 pp. (Nankai Univ. ). Sasayama R. Determination of iron in electrolytic solutions for zinc-bromide batteries. Jpn. Kokai Tokkyo Koho JP 06 27,024 [94 27,0241 (Cl. GOlN21/73) 04 Feb 1994 Appl. 92125,605 13 Feb 1992; 19pp. (Meidensha Electric Mfg. Co. Ltd. Japan). Nishimoto S. Takahashi K. Noguchi Y. Bandai K. Okuno S. Fukuzaki Y. Morita M. Emission spectral analysis of steel. Jpn. Kokai Tokkyo Koho JP 06 88,793 [94 88,7931 (Cl. GOlN23/223) 29 Mar 1994 Appl. 92/263,152,04 Sep 1992; 9 pp.(Kobe Steel Ltd. Japan). Kubota K. Arikane H. Yoshitomi M. Etching method for ultra trace metal analysis on silicon wafer surface. Jpn. Kokai Tokkyo Koho JP 06,213,805 [94,213,805] (Cl. GOlN21/31) 05 Aug 1994 Appl. 9317,047 19 Jan 1993; 4 pp. (Shinnippon Seitetsu Kk Japan). Thuy D. T. Decnop-Weever D. Kok W. Th. Luan P. Nghi T. V. Determination of traces of calcium and magnesium in rare earth oxides by flow-injection analysis. And. Chim. Acta 1994 295 151. (Lab. Anal. Chem. Univ. Amsterdam Nieuwe Achtergracht 166 1018 WV Amsterdam Netherlands). Wang S.-c. Lin K.-c. Novel technique to reduce electrical interference inherent in laser-enhanced ioniz- ation detection by using flow injection analysis. Anal. Chem. 1994 66 2180. (Dept. Chem. Natl. Taiwan Univ. Taipei 10764 Taiwan).Yasuda K. Hirano Y. Kamino T. Hirokawa K. Relationship between the formation of intermetallic compounds by matrix modifiers and atomization in graphite furnace-atomic absorption spectrometry and an observation of the vaporization of intermetallic compounds by means of electron microscopy. Anal. Sci. 1994,10 623. (Instrum. Div. Hitachi Ltd. Katsuta 312 Japan). Kumamaru T. Tao S. Uchida M. Okamoto Y. Electrothermal vaporization of trace gallium via in situ alkylation for inductively coupled plasma atomic emis- sion spectrometry. Anal. Lett. 1994,27 2331. (Fac. Sci. Hiroshima Univ. Higashi-Hiroshima 724 Japan). Chang X.-j. Su Z.-x. Zhan G.-y. Luo X.-y. Gao W.-y. Synthesis and efficiency of a polyacrylacylisothi- ourea chelating fibre for the preconcentration and separation of trace amounts of gold palladium and ruthenium from solution samples.Analyst (London) 1994,119,1445. (Dept. Chem. Lanzhou Univ. Lanzhou 730000 China). Stockwell P. B. Corns W. T. Environmental sensors based on atomic fluorescence. Analyst (London) 1994 119 1641. (P.S. Analytical Ltd. Kemsing UK TN15 Madrid Y. Camara C. Lead hydride generation atomic absorption spectrometry an alternative to electrothermal atomic absorption spectrometry. A review. Analyst (London) 1994,119 1647. (Fac. Quim. Univ. Complutense Madrid 28040 Spain). Platteau O. Casabiell D. Determination of metallic elements in catalysts by flame atomic absorption spectrometry following microwave energy assisted dis- solution of samples. Analyst (London) 1994 119 1705. (Anal.and Eval. Dept. INTEVEP Caracas 1070A Venezuela). Kocjan R. Silica gel modified with zincon as a sorbent for preconcentration or elimination of trace metals. 6QY). 9513652 9513653 9513654 95/3655 9513656 95/3657 9513658 9513659 9513660 9513661 9513662 9513663 9513664 95/3665 Analyst (London) 1994 119 1863. (Dept. Inorg. Anal. Chem. Med. Acad. 20-08 1 Lublin Poland). Funtov V. N. Nemets V. M. Petrov A. A. Soloviov A. A. Isotopic chromatographic spectral analysis of inorganic gases. Appl. Spectrosc. 1994 48 884. (Inst. Phys. St. Petersburg State Univ. St. Petersburg 198904 Russia). Gailer J. Irgolic K. J. Ion-chromatographic behaviour of arsenite arsenate methylarsonic acid and dimethyl- arsinic acid on the Hamilton PRP-X100 anion-exchange column. Appl. Organomet.Chem. 1994 8 129. (Inst. Anal. Chem. Karl Franzens Univ. 8010 Graz Austria). El-Defrawy M. M. Kabil M. A. Ghazy S. E. Characterization and elimination of the interfering effects on flame atomic absorption spectrometric deter- mination of selenium. Analusis 1994 22 350. (Fac. Sci. Mansoura Univ. Mansoura Egypt). Porta L. F. Moyanao S. Villegas 0. I. Lopez R. O. Merodio J. C. Determination of tungsten by atomic absorption spectrometry. 111. Analysis of ores and aqueous concentrates. An. Asoc. Quim. Argent. 1994 82 85. (Fac. Quim. Bioquim. y Farm. Univ. Nacl. San Luis San Luis Argentina). Schneider C. A. Schulze H. Baasner J. McIntosh S. Hanna C. Optimizing mercury determinations. Am. Lab. (Shelton Conn.) 1994 26 18. (Perkin-Elmer Corp. Norwalk CT 06859-0291 USA).Li G.-k. Zhang Z.-x. Yang X.-h. Standardless analysis by graphite furnace AAS. 111. Stability of the experimen- tal characteristic mass. Fenxi Ceshi Xuebao 1994 13 44. (Dept. Chem. Zhongshan Univ. Guangzhou 510275 China). Zheng J.-g. Zhou Q. Oian H.-w. Zhang Z.-x. Application of internal standard method in ICP-AES. 1. Signal correlation and improvement of analytical precision. Fenxi Ceshi Xuebao 1994 13 28. (Dept. Chem. Zhongshan Univ. Guangzhou 510275 China). Pauwels J. Hofmann C. Vandecasteele C. On the usefulness of SS-ZAAS for the microhomogeneity control of CRM’s. Fresenius’ J. Anal. Chem. 1994 348 418. (Inst. Ref. Mater. and Measure. Joint Res. Centre B-2440 Geel Belgium). Mierzwa J. Dobrowolski R. Silica gel analysis by slurry sampling graphite furnace atomic absorption spectrometry. Fresenius’ J.Anal. Chem. 1994 348 422. (Central Lab. Maria Curie-Sklodowska Univ. PL-20031 Lublin Poland). Stock H.-R. Hoehl F. Mayr P. Calibration standards for composition-depth profiles of non-stoichiometric titanium nitride coatings. Fresenius ’ J. Anal. Chem. 1994,349,208. (Stiftung Inst. Werkstofftechnik D-28359 Bremen Germany). Erber D. Quick L. Winter F. Roth J. Cammann K. Wickbold combustion method for the determination of mercury under statistical aspects. Fresenius’ J. Anal. Chern. 1994 349 502. (Inst. Chem. Biosensorik Westfaelische Wilhelms-Univ. D-48 149 Munster Germany). Kawabe I. Inoue T. Kitamura S. Comparison of REE analyses of GSJ carbonate reference rocks by ICP-AES and INAA fission and spectral interferences in INAA determination of REE in geochemical samples with high U/REE ratios.Geochem. J. 1994,28 19. (Fac. Sci. Ehime Univ. Matsuyama 790 Japan). Yang P.-y. Wang X.-r. Yin H. Deng Z.-w. Wang Z.-y. Non-local thermal equilibrium in ICP-AES. I. Non-Boltzmann distribution in excitation. Guangpuxue Yu Guangpu Fenxi 1993 13(5) 63. (Dept. Chem. Xiamen Univ. Xiamen 361005 China). Zheng J.-g. Zhang Z.-x. Monte Carlo technique for studying chemical and physical processes in ICP-AES. I. Simulation of evaporation process. Guangpuxue Yu Guangpu Fenxi 1994 14(3) 53. (Dept. Chem. Zhongshan Univ. Guangzhou 5 10275 China). Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 339R9513666 9513667 9513668 9 513 669 9513670 9513671 9513672 9513673 9513674 9 513 67 5 9513676 9 513 677 9513678 9513679 9513680 95/3681 340 R Zhu C.-f.Wu Q. Analysis of metal impurity in high- purity chemical reagents. Guangpuxue Yu Guangpu Fenxi 1994 14( 3) 71. (Elect. Mater. Charact. Centre Mach. and Elect. Minist. Tianjing 300192 China). Wang F.-y. Wan J.4. Mechanisms of enhancement and interference suppression effect of surfactants in flame atomic absorption spectrometry. Guangpuxue Yu Guangpu Fenxi 1994 14(3) 79. (Centre Anal. Testing Central China Normal Univ. Wuhan 430070 China). Bao S.-y. Shi S.-x. Application on atomic absorption spectrometry to the analysis of molecular spectra. I. Study on theory and techniques. Guangpuxue Yu Guungpu Fenxi 1994 14(3) 121. (Dept. Chem. Heibei Univ. Boading 071002 China). Yang P.-y. Ying H. Wang X.-r. Deng Z.-w.Zhu E.-y. ICP-AES inquiring system for selection of analyt- ical spectral lines. Jisuanji Yu Yingyong Huaxue 1994 11 146. (Dept. Chem. Xiamen Univ. Xiamen 361005 China). Liu Y. Lopez-Avila V. Alcaraz M. Beckert W. F. Simultaneous determination of organotin organolead and organomercury compounds in environmental samples using capillary gas chromatography with atomic emission detection. J. High Resolut. Chromatogr. 1994 17 527. (California Operation Midwest Res. Inst. Mountain View CA 94043 USA). Feng Z.-g. Zhang H.-j. Tang M.-h Spectrochemical determinaiton of trace gold in samples with electrolysis preconcentration. Kuangwu Yanshi 1994 14,98. (Dept. Appl. Chem. Chengdu Inst. Tech. Chengdu 610059 China). Suzuki S.-g. Guide to analysis of metal materials.Isolated atom analysis on surfaces. Kinzoku 1994 64 60. (Nippon Steel Corp. Futtsu 299-12 Japan). Kawano H. Nakamoto M. Kuroda D. ICP-atomic emission spectrophotometry. Kagaku to Kogyo (Osaka) 1993 67 514. (Osaka Munic. Tech. Res. Inst. Osaka 536 Japan). Karim M. R. O. Karadaghi T. M. Najib F. M. Determination of nanomole quantities of lower alde- hydes by cold-vapour atomic absorption spectrometry. Mikrochim. Acta 1994 116 57. (Coll. Sci. Salahaddin Univ. Erbil Iraq). Zhang Q.-t. Shen D.-w. Wang G.-h. Hydride atomic absorption spectrometry for trace Se in monominerals. Nanjing Huagong Xueyuan Xuebao 1994,16 53. (Dept. Mater. Sci. Eng. Nanjing Inst. Chem. Technol. Nanjing 210009 China). Wu Y.-l. Jiang X.-d. Determination of aluminium by atomic absorption spectrometry.Nanjing Huagong Xueyuan Xuebao 1994 16 84. (Dept. Appl. Chem. Nanjing Inst. Chem. Technol. Nanjing 210009 China). Oki Y. Tad T. Kidera N. Maeda M. Trace element analysis by laser ablation atomic fluorescence spec- troscopy. Opt. Commun. 1994 110 298. (Dept. Electr. Eng. Kyushu Univ. Higashi-ku Fukuoka 812 Japan). Groll Kh. Zybin A. B. Nimaks K. Shnyurer-Pachan K. Diode lasers in atomic-absorption analytical spec- troscopy lowering detection limits through the measure- ment of low absorption. Opt. Spektrosk. 1994 76 502. (Inst. Spektrosk. Troitsk 142092 Russia). Giles R. Sullivan J. L. Pearce C. G. Design and development of a time-of-flight fast atomlion scattering spectrometer. Surf Interface Anal. 1994,22 576. (Aston Univ. Birmingham UK). Zander A. T. Fifty years of commercial instrumentation in atomic emission spectrometry.Spectroscopy (Eugene Oreg.) 1994 9 16. (E. L. Ginzton Res. Centre Varian Assoc. Inc. Palo Alto CA 94304-1025 USA). Di P. Davey D. E. Trace gold determination by online preconcentration with flow injection atomic absorption spectrometry. Talanta 1994 41 565. (Sch. Chem. Technol. Univ. South Australia The Levels 5095 Australia). 9513682 9513683 9513684 95/3685 9513686 9513687 9513 68 8 9513689 9513690 9513691 9513692 9513693 9513694 9513695 Otruba V. Stepankova J. Sommer L. Selective preconcentration of thallium on modified silica gel for its determination by flame emission and absorption spectrometry. Talanta 1994 41 1185. (Dept. Anal. Chem. Masaryk Univ. Brno 611 37 Czech Republic). Venkaji K. Naidu P.P. Rao T. J. P. Determination of tin bismuth antimony indium gallium and arsenic by solvent extraction and atomic absorption spectro- photometry. Talanta 1994,41 1281. (Geol. Surv. India Bangalore 560041 India). Guo R.-d. Jiang X.-f. Determination of tin in unplas- ticked polyvinyl chloride pipes for drinking water supply by Zeeman effect graphite furnace atomic absorption. Weisheng Yunjiu 1994 23 83. (Jiangsu Province Sanitation Antiepidemic Station Nanjing 210009 China). Yang S.-y. Huang Y.-h. Chemical spectrographic determination of trace elements in high-purity gold. Xiyou Jinshu Cailiao Yu Gongcheng 1994 23 69. (Northwest Inst. Nonferrous Metal Res. Baoji 721014 China). Lin SA. Qiu H.-o. Tang Z.-y. Determination of antimony by flow injection-hydride generation atomic fluorescence spectrometry - vapour collection and pulsed sampling technique. Yankuang Ceshi 1994 13 113.(Dept. Appl. Chem. China Univ. Geosciences Wuhan 430074 China). Zhou X.4. Determination of sulfur by molecular absorption spectrometry of aluminium sulfide with volatilization in a graphite furnace. Yankuang Ceshi 1994 13 118. (Shanghai Inst. Electr. Power Shanghai 200090 China). Toronov 0. G. Analysis of high-alloy steels with the DFS-51 spectrometer. Zavod. Lab. 1994,60,25. (MGP St. Petersburg Russia). Chatterjee A. Das D. Mandal B. K. Chowdhury T. R. Samanta G. Chakraborti D. Arsenic in ground water in six districts of West Bengal India the biggest arsenic calamity in the world. Part 1. Arsenic species in drinking water and urine of the affected people. Analyst (Cambridge UK) 1995 120 643.(Sch. Environmental Stud. Jadavpur Univ. Calcutta 700032 India). Jervis R. E. Krishnan S. S. KO M. M. Vela L. D. Pringle T. G. Chan A. C. Lu X. Biological incinerator emissions of toxic inorganics their residues and their availability. Analyst (Cambridge UK) 1995 120 651. (Dept. Chem. Eng. and Appl. Chem. and Inst. Environ. Stud. Univ. Toronto Toronto Ontario Canada M5S 1A4). Kuballa J. Wilken R.-D. Jantzen E. Kwan K. K. Chau Y. K. Speciation and genotoxicity of butyltin compounds. Analyst (Cambridge UK) 1995 120 667. (GKSS Res. Centre Inst. Chem. Max-Planck-Str. D-21502 Geesthacht Germany). Sanz-Medel A. Beyond total element analysis of biological systems with atomic spectrometric tech- niques. Analyst (Cambridge UK) 1995,120,799. (Dept.Phys. and Anal. Chem. Fac. Chem. Univ. Oviedo 33006 Oviedo Spain). Wrobel K. Blanco Gonzalez E. B. Wrobel K. Sanz- Medel A. Aluminium and silicon speciation in human serum by ion-exchange high-performance liquid chrom- atography-electrothermal atomic absorption spec- trometry and gel electrophoresis. Analyst (Cambridge UK) 1995 120 809. (Dept. Phys. and Anal. Chem. Fac. Chem. Univ. Oviedo 33006 Oviedo Spain). Zaichick V. Ye. Tsyb A. F. Vtyurin B. M. Trace elements and thyroid cancer. Analyst (Cambridge UK) 1995 120 817. (Med. Radiol. Res. Centre Obninsk 249020 Kaluga Region Russia). MacPherson A. Balint J. Bacso J. Beard calcium concentration as a marker for coronary heart disease as affected by supplementation with micronutrients Journal of Analytical Atomic Spectrometry November 1995 Vol.109513696 9513697 9513698 9513699 9513700 9513701 9513702 9513703 95/3704 9513705 9513706 9513707 including selenium. Analyst (Cambridge UK) 1995 120 871. (Biochem. Sci. SAC Auchincruive Ayr Scotland UK KA6 5HW). Luppino M. A. McLean A. J. Plasma and tissue distribution of bismuth in normal and cirrhotic rats. Analyst (Cambridge UK) 1995 120 883. (Dept. Clin. Pharmacol. Alfred Hosp. Commercial Rd. Prahran Victoria 3181 Australia). Williams N. R. Rajput-Willians J. West J. A. Nigdikar S. V. Foote J. W. Howard A. N. Plasma granulocyte and mononuclear cell copper and zinc in patients with diabetes mellitus. Analyst (Cambridge UK) 1995 120 887. (COAG Trace Elements Lab. Pathol. Dept. Papworth Hosp. NHS Trust Cambridge UK CB3 8RE).Das D. Chatterjee A. Mandal B. K. Samanta G. Chakraborti D. Chanda B. Arsenic in ground water in six districts of West Bengal India the biggest arsenic calamity in the world. Part 2. Arsenic concentration in drinking water hair nails urine skin-scale and liver tissue (biopsy) of the affected people. Analyst (Cambridge UK) 1995 120 917. (Sch. Environ. Stud. Jadavpur Univ. Calcutta 700032 India). Luterotti S. Matrix effects in the determination of zinc@) ion in whole rat liver by flame atomic absorption spectrometry. Analyst (Cambridge UK) 1995,120 925. (Dept. Anal. Chem. Fac. Pharmacy and Biochem. Univ. Zagreb A Kovacica 1 41000 Zagreb Croatia). Chlopicka J. Zagrodzki P. Zachwieja Z. Krosniak M. Folta M. Use of pattern recognition methods in the interpretation of heavy metal content (lead and cadmium) in children’s scalp hair.Analyst (Cambridge UK) 1995 120 943. (Dept. Food Chem. and Nutr. Coll. Med. Jagiellonian Univ. Podchorqzych 1 30-084 Cracow Poland). Moreira M. de F. R. Curtius A. J. Calixto de Campos R. Determination of cadmium in whole blood and urine by electrothermal atomic absorption spectrometry using palladium-based modifiers and in-situ decontami- nation. Analyst (Cambridge UK) 1995 120 947. (Fundacao Osvaldo Cruz Rio de Janeiro Brazil). Thunus L. Dauphin J. F. Moiny G. Deby C. Deby- Dupont G. Anti-inflammatory properties of copper gold and silver individually and as mixtures. Analyst (Cambridge UK) 1995 120 967. (Lab. Chim. Anal. Inst. Pharm. Fly Univ. Liege 3 rue Fusch B-4000 Liege Belgium).Tsipouras N. Rix C. J. Brady P. H. Solubility of silver sulfadiazine in physiological media and relevance to treatment of thermal burns with silver sulfadiazine cream. Clin. Chem. ( Winston-Salem N. C . ) 1995 42 87. (Dept. Appl. Chem. Royal Melbourne Inst. Technol. GPO Box 2476V Melbourne Victoria 3001 Australia). Bush V. J. Moyer T. P. Batts K. P. Parisi J. E. Essential and toxic element concentrations in fresh and formalin-fixed human autopsy tissues. Clin. Chem. (Winston-Salem N. C.) 1995 41 284. (Div. Clin. Biochem. Dept. Lab. Med. and Pathol. Mayo Clinic Rochester MN 55905 USA). Verebey K. Rosen J. F. Schonfeld D. J. Carriero D. Eng Y. M. Deutsch J. Reimer S. Hogan J. Blood collection and analytical considerations in blood lead screening in children.Clin. Chem. ( Winston-Salem N. C.) 1995 41 469. (New York State Inst. Basic Res. OMRDD Staten Island NY USA). Faux S. P. Gao M. Aw T. C. Braithwaite R. A. Levy L. S. Molecular epidemiological studies in workers exposed to chromium-containing compounds. Clin. Chem. ( Winston-Salem N. C.) 1994 40 1454. (Inst. Occup. Health Univ. Birmingham Edgbaston Birmingham UK B15 2TT). Milne D. B. Assessment of copper nutritional status. Clin. Chem. ( Winston-Salem N. C . ) 1994 40 1479. (Grand Forks Human Nutrition Res Center Agric. Res. Service US Dept. Agric. Grand Forks ND 58202-9034 USA). 9513708 9513709 95/37 10 951371 1 9513712 9513713 9513 7 14 951371 5 95/37 16 9513717 95/3718 95/3719 9513720 951372 1 Savory J. Iatrogenic aluminium poisoning. Clin. Chem. ( Winston-Salem N.C.) 1994 40 1477. (Dept. Pathol. and Biochem. Univ. Virginia Health Sci. Center Charlottesville VA 22908 USA). Al-Saleh I. Devol E. Taylor A. Distribution of blood lead levels in 1,047 Saudi Arabian children with respect to province sex and age. Arch. Environ. Health 1994 49 471. (Biol. and Med. Res. Dept. King Faisal Specialist Hosp. and Res. Centre Riyadh Saudi Arabia). Takenaka H. Pponma Y. Ishii Y. Maruo T. Kawamura T. Standard substances for secondary ion mass spectrometry. Jpn. Kokai Tokkyo Koho JP 06,273,289 [94,273,289] (Cl. GOlN1/00) 30 Sep 1994 Appl. 93/60,640 19 Mar 1993; 7 pp. (Nippon Telegraph & Telephone Japan). Hashiguchi H. Tanaka Y. Maeda S. Determination of surface atomic distribution of solid samples and apparatus therefore. Jpn.Kokai Tokkyo Koho JP 06,331,634 [94,331,634 J (Cl. G01N37/00) 02 Dec 1994 Appl. 931119,633 21 May 1993; 6 pp. (Shinnippon Seitetsu Kk Japan). Chao K.-j. Lin LA. Ling Y.c. Hwang J.-f. Hou L.-y. Vanadium passivation on cracking catalysts by imaging secondary ion mass spectrometry. Appl. Catal. A 1995 121 217. (Dept. Chem. Tsinghua Univ. Hasinchu Taiwan 30043 Taiwan). Sone J. H. Moon J. Kim H. J. Study on the interface of LPCVD-W and SiO Control Semicond. Interfaces Proc. Int. Symp. 1 st 1993. Elsevier Amsterdam Netherlands 1994. 429. Stephan T. Jessberger E. K. Kloeck W. Rulle H. Zehnpfenning J. TOF-SIMS analysis of interplanetary dust. Earth Planet. Sci. Lett. 1994 128 453. (Max- Planck-Inst. Kernphys. Postfach 103980 D-69029 Heidelberg Germany). Kudryavtsev Yu. A.Yagovkima M. A. Kovarskii A. P. Study of yield of sputtered neutrals from A3B5 semiconducting compounds. Izv. Akad. Nauk Ser. Fiz. 1994 58 170. (Inst. Mater. Probl. Biol. Pushchino Russia). Mel’nikov V. N. Belous T. P. Volodchenko V. S. SIMS investigation of GaN surface exposed to oxygen in vacuum. Izv. Akad. Nauk Ser. Fiz. 1994 58 63. (Khar’k. Gos. Univ. Kharkov Ukraine). Berardi V. Amoruso S. Spinelli N. Armenante M. Velotta R. FUSO F. Allegrini M. Arimondo E. Diagnostics of YB~&U~O.,-~ laser plume by time-of- flight mass spectrometry. J. Appl. Phys. 1994,76 8077. (Dip. Sci. Fis. Univ. degli Studi Federico 11 1-80125 Naples Italy). Chu P. K. Bleiler R. J. Metz J. M. Determination of sub-parts per billion boron contamination in N+ Czochralski silicon substrates by SIMS.J. Electrochem. SOC. 1994 141 3453. (Charles Evans Assoc. Redwood City CA 94063 USA). Kyoh S. Takakuwa K. Sakura M. Umezawa M. Itoh A. Imanishi N. Multiple-charged secondary-ion emission from silicon and silicon oxide bonbarded by heavy ions at energies of 0.4-10 MeV. Phys. Rev. A At. Mol. Opt. Phys. 1995 51 554. (Dept. Nucl. Eng. Kyoto Univ. Kyoto 606-01 Japan). Bulgakov A. V. Mayorov A. P. Predtechensky M. R. Kozlov B. N. Pilyugin I. L. Shchebelin V. G. Cluster formation in the laser-induced plume created above YBaCuO superconductor. Prog. Astronaut. Aeronaut. 1994 158 3 11. (Inst. Thermophys. Novosibirsk Russia). Quadakkers W. J. Elschner A. Zheng N. Schuster H. Nickel H. SNMS investigations concerning the effect of niobium additions on the oxidation behaviour of titanium aluminides Microsc.Oxid. 2 Proc. Int. Conf. 2nd. Inst. Mater. London UK 1993. 488. Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 341 R9513722 9513723 9 513 724 9513725 9513726 9513727 9 513 728 9513729 9513730 9513731 9513732 9 5/c 3 73 3 9 5/c 3 7 34 342 R Bishop H. E. Application of dynanlic secondary ion mass spectrometry to the study of oxidation Microsc. Oxid. 2 Proc. Int. Conf. 2nd. Inst. Mater. London UK 1993. 14. Gil A. Jedlinski J. Slowik J. Borchardt G. Mrowec S. Contribution of the water vapour-induced effects to SIMS-spectra from scales growing on chromium during isotopic exposures Microsc. Oxid. 2 Proc. Int. Con$ 2nd. Inst. Mater. London UK 1993. 214. Liu J. Gale R. J. Secondary ion mass spectrometry of room-temperature chloroborate and mixed chloro- boratelchloroaluminate melts.Proc.-Electrochem. SOC. 1993 93 90. (Dept. Chem. Louisiana State Univ. Baton Rouge LA 70803 USA). Pitts L. Fisher A. Worsfold P. Hill S. J. Selenium speciation using high-performance liquid chromatogra- phy - hydride generation atomic fluorescence with on-line microwave reduction. J. Anal. At. Spectrom. 1995 10 519. (Dept. Environ. Sci. Univ. Plymouth Drake Circus Plymouth UK PL4 8AA). Tang S. Parsons P. J. Slavin W. Effect of acids modifiers and chloride on the atomization of aluminium in electrothermal atomic absorption spectrometry. J. Anal. At. Spectrom. 1995 10 521. (Dept. Environ. Health and Toxicol. Sch. Public Health State Univ. of New York at Albany Albany NY 12201 USA).Brown G. N. Styris D. L. Hinds M. W. Mechanisms controlling direct solid sampling of silicon from gold samples by electrothermal atomic absorption spec- trometry. Part 2. Atomization from aqueous and solid samples. J. Anal. At. Spectrom. 1995 10 527. (Pacific Northwest Lab. Box 999 Richland WA 99352 USA). Chen H.-w. Xu S.-k. Fang 2.4. Electrothermal atomic absorption spectrometric determination of molybdenum in water human hair and high-purity reagents with flow injection on-line coprecipitation preconcentration. J. Anal. At. Spectrom. 1995 10 533. (Flow Injection Anal. Res. Centre Inst. Appl. Ecol. Acad. Sin. 110015 Shenyang China). Enger J. Marunkov A. Chekalin N. Axner 0. Direct detection of antimony in environmental and biological samples at trace concentrations by laser-induced fluo- rescence in graphite furnace with an intensified charge coupled device.J. Anal. At. Spectrom. 1995 10 539. (Anal. Laser Spectrosc. Group Dept. Phys. Chalmers Univ. Technol. S-41296 Goteborg Sweden). Lam J. W. H. McLaren J. W. Methven B. A. J. Determination of chromium in biological tissues by inductively coupled plasma mass spectrometry. J. Anal. At. Spectrom. 1995 10 551. (Natl. Res. Council Canada Inst. Environ. Res. and Technol. Ottawa Canada K1A OR6). Bettinelli M. Spezia S. Baroni U. Bizzarri G. Determination of trace elements in fuel oils by induc- tively coupled plasma mass spectrometry after acid mineralization of the sample in a microwave oven. J. Anal. At. Spectrom. 1995 10 555. (ENEL S.p.a. DCO-Central Lab. Via Nino Bixio 29100 Placenza It a1 y) .Hill S. J. Dawson J. B. Price W. J. Shuttler I. L. Tyson J. F. Atomic spectrometry update - advances in atomic absorption and fluorescence spectrometry and related techniques. J. Anal. At. Spectrom. 1995 10 199. (Dept Environ. Sci. Univ. Plymouth Drake Circus Plymouth UK PL4 8AA). Havranek V. Hnatowicz V. Perina V. Vosecek V. Analyses of the solids with H and He ion beams at NPI. 10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Nucl. Phys. Inst. 250 68 Rez Czech Republic). Gregoire D. C. Chakrabarti C. L. Goltz D. M. Hughes D. M. Trace micro-analysis by electrothermal vaporization ICP mass spectrometry. 10th Spectro- 95/c3 73 5 951C3736 95/c3 73 7 9 5/C37 3 8 95/c3 739 951c3740 95/c3 74 1 951c3742 9 51c3743 95/c3 744 9 5/c3 745 951C3746 951c3747 Journal of Analytical Atomic Spectrometry November 1995 Vol.10 scopic Conference Lanskroun Czech Republic June 14-16 1995 (Geol. Surv. Canada 601 Booth St. Ottawa Ontario Canada K1A OE8). Dedina J. Hydride atomization for AAS - current state and perspectives. 10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Inst. Anal. Chem. Lab. Trace Element Anal. Acad. Sci. Czech Republic Prague Czech Republic). L’vov B. V. Recent advances in calibration for Zeeman GFAAS. 10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Dept. Anal. Chem. St. Petersburg Tech. Univ. St. Petersburg 195251 Russia). Hoenig M. Present status of electrothermal atomic absorption spectrometry in the arsenal of atomic spectroscopy techniques.10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Centre Etudes et Rech. Vet. et Agrochim. Minist. Agric. (CERVA) Leuvensesteenweg 17 3080 Tervuren Belgium). Welz B. Gilmutdinov A. Kh. Sperling M. Spatially resolved spectroscopy in graphite atomizers - or rewriting Beer’s law for GFAAS. 10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Dept. Appl. Res. Bodenseewerk Perkin-Elmer GmbH D-88647 Uberlingen Germany). Sysalova J. Skopkova I. Investigation of blood lead levels in a Czech general population using GFAAS. 10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Inst. Anal. Chem. Czech Acad. Sci. Videnska 1083 142 20 Prague 4 Czech Republic). Spevackova V. Kratzer K. Determination of selected elements in blood and urine for the monitoring purposes. 10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Inst.Public Health Srobarova 48 100 42 Prague 10 Czech Republic). Beran M. Kelnar L. Sara V. Determination of some toxic and essential elements in mushrooms and blue- berries using atomic absorption spectrometry. 10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Central Anal. Lab. Nucl. Res. Inst. Rez Rez Czech Republic). Kanicky V. Mermet J.-M. Analysis of glass using laser ablation - inductively coupled plasma atomic emission spectrometry. 10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Dept. Anal. Chem. Masaryk Univ. Brno Czech Republic). Parosa R. Reszke E. Ramsza A. Helan V.Novel systems of microwave digestion. 10th Spectroscopic Conference Lanskroun Czech Republic June 14- 16 1995 (Plazmatronika Wroclaw Poland). Cernohorsky T. Dolezal J. Hlavac R. Vyskocilova 0. Optimum conditions for UV-mineralization of solutions. 10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Dept. Environ. Prot. Univ. Pardubice Czech Republic). Matousek T. Dedina J. Mechanism of interferences in selenium hydride atomization in quartz tubes for AAS. 10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Inst. Anal. Chem. Lab. Trace Element Anal. Acad. Sci. Czech Republic Videnska 1083 142 20 Prague Czech Republic). Docekal B. New approaches in the direct analysis of high purity molybdenum-based materials. 10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Inst.Anal. Chem. Czech Acad. Sci. Veveri 97 CZ-61142 Brno Czech Republic). Cernohorsky T. Canova L. Analysis of samples with high content of salts by FIA-FAAAS. 10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Univ. Pardubice Cs. Legii 565,532 10 Pardubice Czech Republic).9 5/C 3 748 951c3749 951c3750 951c3751 951c3752 95lC3753 9 5/c37 54 951c3755 95lC3756 95/c 3 7 57 9 5/C375 8 951c3759 951C3760 Novotny K. Turzikova A. Komarek J. Speciation of copper using Donnan dialysis and FAAS. 10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Dept. Anal. Chem. Masaryk Univ. Brno Czech Republic). Rychlovsky P. Krenzelok M. Volhejnova R. On-line simultaneous sorption preconcentration and determi- nation of Cr(II1) and Cr(1v) with AAS detection.10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Dept. Anal. Chem. Charles Univ. Albertov 2030 CZ-128 43 Prague 2 Czech Republic). Krenzelok M. Rychlovsky P. Brzakova S. Separation and determination of organotin compounds by HPLC with AAS detection. 10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Dept. Anal. Chem. Charles Univ. Albertov 2030 CZ-128 43 Prague 2 Czech Republic). Moskalova M. Zemberyova M. Hutta M. Resolution and determination of mercury and methylmercury in environmental samples by trace mercury analyser-TMA 254. 10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Dept. Anal. Chem. Fac. Nat. Sci. Comenius Univ.842 15 Bratislava Czech Republic). Boruvka L. Kristoufkova S. Kozak J. Cd Pb and Zn content in plants grown on heavily contaminated soils. 10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Dept. Soil Sci. and Geol. Czech Univ. Agric. Prague Czech Republic). Kombercova V. Rejnek J. Novobilsky V. Human hair - information source about loading of human organism by arsenic. 10th Spectroscopic Conference Lanskroun Czech Republic June 14-16,1995 (Teacher Training Fac. Univ. J. E. Purkyne 400 96 Usti nad Labem Czech Republic). Fisera M. Rosenberg M. Hladky Z. Kristofikova L. Determination of selenium in yeast by atomic spec- trometry methods. 10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Inst. Mater. Tech. Univ. Bmo Veslarska 230 637 00 Brno Czech Republic).Korunova V. Selecka A. Determination of selenium and mercury in blood serum in districts Prague-East and Jindrichuv Hradec. 10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Inst. Anal. Chem. Lab. Trace Element Anal. Acad. Sci. Czech Republic Prague Czech Republic). Kalny D. Havel J. Elimination of spectral and/or other interferences in ICP-AES comparison of slim and multivariate calibration approach. 10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Dept. Anal. Chem. Masaryk Univ. Brno Czech Republic). Kucera J. Lener J. Soukal L. Horakova J. Air pollution and biological monitoring of occupational and environmental exposure to vanadium using neutron activation analysis. 10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Nucl.Phys. Inst. Acad. Sci. Czech Republic CZ-250 68 Rez Czech Republic). Zhuk L. I. Kist A. A. Danilova E. A. Mikholskaya I. N. Human hair elemental composition - possible diagnostic tool? 10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Inst. Nucl. Phys. Tashkent Ulughbek 7021 32 Uzbekistan Commonwealth of Independent States (CIS)). Gedeon O. Hulinsky V. Jurek K. Simeckova M. X-ray microanalysis of light and stratified samples. 10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Dept. Glass and Ceramics Inst. Chem. Technol. Prague Czech Republic). Frana J. Mastalka A. Jiran L. Moucha V. INAA and XRF analyses of archaeological bronzes from 951C3761 9513762 9513763 9 513 764 9513765 9513766 9513767 9513768 9 513 769 9513770 951377 1 9513772 9513773 9513774 Bohemia. 10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Nucl. Phys.Inst. Rez Czech Republic). Jurek K. Hulinsky V. Gedeon 0. Migration of alkali atoms in silica glass at X-ray microanalysis. 10th Spectroscopic Conference Lanskroun Czech Republic June 14-16 1995 (Inst. Phys. Acad. Sci. Czech Republic Prague Czech Republic). Malczewski M. L. Demmin H. C. Brown D. E. Wiltse D. R. Gas emission spectrometer and method. Eur. Pat. Appl. EP 617,274 (Cl. GOlN21/69) 28 Sep 1994 US Appl. 36,163 24 Mar 1993; 1Opp. (Praxair Technol. Inc. USA). Etsuno Y. Ubukawa A. Analysis for impurities in optical materials by high-frequency plasma atomic emission spectrometry.Jpn. Kokai Tokkyo Koho JP 06,242,004 [94,242,004] (Cl. GOlN21/73) 02 Sep 1994 Appl. 93127,740 17 Feb 1993; 5 pp. (Ngk Insulators Ltd. Japan). Jinoka T. Takehara H. Concentration and quantita- tion method for metal ions. Jpn. Kokai Tokkyo Koho JP 06,230,002 [94,230,002] (Cl. GOlN31/00) 19 Aug 1994 Appl. 93114,559 01 Feb 1993; 5pp. (Hitachi Ltd. Japan). Mega T. Quantitative analysis of top plating layer of Zn-plated steel sheet by coulomb-discharge atomic emission spectrometry. Jpn. Kokai Tokkyo Koho JP 06,222,004 [94,222,004] (Cl. GOlN21/67) 12 Aug 1994 Appl. 93112,401 28 Jan 1993; 5 pp. (Kawasaki Steel Co. Japan). Cheskis S. Kovalenko S. A. Detection of atomic oxygen in flames by absorption spectroscopy. Appl. Phys. B Lasers Opt. 1994 59 543. (Sackler Fac.Exact Sci. Tel Aviv Univ. 69978 Tel Aviv Israel). Friese K.-C. Krivan V. Analysis of silicon nitride powders for Al Cr Cu Fe K Mg Mn Na and Zn by slurry-sampling electrothermal atomic absorption spec- trometry. Anal. Chem. 1995 67 354. (Sekt. Anal. und Hoechstreinigung Univ. Ulm D-89069 Ulm Germany). Zhu Z.4 Gu Z.-c. Chen R.-m. Han C.q. Lu B.4. Simultaneous determination of catalysts based on the differences in the characteristic rate spectra of catalytic kinetics. Anal. Chim. Acta 1994 298 19. (Dept. Chem. TongJi Univ. Shanghai China). Teneva M. Tsvetkova D. Petrova M. Atomic emission spectrometric determination of high concentration chemical elements in copper alloys. Anal. Lab. 1994 3 94. (Inst. Metalscience 1574 Sofia Bulgaria). Momchilova E. Koleva S.Malcheva V. Research of the matrix influence in atomic absorption determination of manganese in aluminium alloys. Anal. Lab. 1994 3 105. (Inst. Metal Science 1574 Sofia Bulgaria). Crooks W. J. 111 Choppin G. R. General technique for heteropolyanion analysis using inductively coupled plasma atomic emission spectroscopy atomic absorp- tion spectroscopy and gravimetry. Anal. Lett. 1994 27 2737. (Dept. Chem. Florida State Univ. Tallahassee Imai S. Ibe T. Tanaka T. Hayashi Y. Atomization mechanism of gallium in graphite furnace atomic absorption spectrometry. Anal. Sci. 1994 10 901. (Dept. Chem. Joetsu Univ. Educ. Nigata 943 Japan). Eid M. A. Analytical plasma sources for optical emission spectroscopy. Bilateral Semin. Int. Bur. 1994 15 225. (Spectrosc. Dept. Natl. Res.Centre Cairo Garten R. P. H. Analytical methods used in determining trace elements in environmental matter. Bilateral Semin. Int. Bur. 1994 19 89. (Labor Reinststoffanal. Max-Planck-Inst. Metallforsch. D-44139 Dortmund Germany). FL 32306-3006 USA). Egypt). Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 343R9 513 775 9513776 9513777 9513778 9513779 9513780 9513781 9513782 9513783 9 513 7 84 9513785 9513786 9 513 787 9513 78 8 9 513 7 8 9 344R Boehm H. Characterization of coated steel sheets with a glow discharge spectrometer. Blech Rohre Profile 1994 41 375. (Spectrosc. Div. Leco Instrum. GmbH D-85551 Kirchheim Germany). Ibrahim J. M. Spectroscopic study of some arc parameters of anode and cathode excitation. Bull. Nut. Res. Cent. Egypt 1994 19 59.(Spectrosc. Dept. Natl. Res. Centre Cairo Egypt). Schulze H. Baasner J. Fully automated mercury trace analysis with flow-injection cold vapour AAS. Chem.- Anlangen Verfahren 1994 27 92. (Germany). Liang F. Zhang H.-q. Jin Q.-h. On-line anion exchange preconcentration in microwave plasma torch atomic emission spectrometry. Chem. Res. Chin. Uniu. 1994 10 43. (Dept. Chem. Jilin Univ. Changchun 130032 China). Postma G. J. Hack F. M. Janssen P. A. A. Buydens L. M. C. Kateman G. Database approach on analytical chemical methods applying fuzzy logic in the search strategy and flow charts for the representation of the retrieved analytical procedures. Chemom. Intell. Lab. Syst. 1994 25 285. (Dept. Anal. Chem. Katholieke Univ. Nijmegen Toernooiveld 1 6525 ED Nijmegen Netherlands).Zander A. T. Meeting the technology requirements of atomic absorption spectrophotometry. Chem. Aust. 1994 61 190. (Varian Res. Centre Palo Alto CA 94304 USA). Li Y.-g. Atomic absorption spectrometric determi- nation of trace cadmium in passivation solution for cadmium plating. Diandu Yu Tushi 1994 13 48. (Wangjiang Machinery Co. Chongqing 630071 China). Lu T. Zhong Y.-l. Liang S.-h. Device for continuous monitoring of gradient elution extraction chromatogra- phy with post-column spectrometry. Fenxi Ceshi Xuebao 1994 13 1. (Inst. Chem. Chin. Acad. Sci. Beijing 100080 China). Wang H.-n. Chen Y. Liu Z.-h. Wang J. Sampling method for improving the sensitivity of determining iodide by inductively coupled plasma atomic emission spectroscopy. Fenxi Ceshi Xuebao 1994 13 71.(Anal. and Measure. Centre Harbin Inst. Technol. Harbin 150001 China). Hou X.d. Li C.-r. Zhang H.-p. Su Q.-p. Separation and preconcentration of trace palladium with thiosem- icarbazide cellulose column. Fenxi Huaxue 1994 22 532. (Dept. Appl. Chem. Chengdu Univ. Sci. Technol. Chengdu China). Cai Y.-q. Zhu Q.-c. Determination of boron by indirect flame atomic absorption spectrometry. Fenxi Huaxue 1994 22 752. (Inst. Chem. Qufu Normal Univ. Qufu China). Wang H.-n. Yao C. Determination of trace arsenic in copper alloy by on-line flow injection-hydride gener- ation inductively coupled plasma atomic emission spectrometry. Fenxi Huuxue 1994 22 816. (Anal. and Measure. Centre Harbin Univ. Technol. Harbin 150006 China). Zhuang Y.-q. Analysis for impurity elements in pure scandium oxide by atomic emission spectrometry.Fenxi Huaxue 1994 22 859. (Rare Earth Inst. Baotou Iron and Steel Co. Batou 01410 China). Richter J. Wycislik A. Cwajna J. Investigations of the carbide phase and the matrix of non-ledeburitic high-speed steel with Ti and Nb by atomic absorption spectrometry and energy dispersive X-ray spectroscopy methods. Fresenius’ J. Anal. Chem. 1994 349 153. (Salesian Tech. Univ. Katowice Poland). Bobruiko V. B. Glavin G. G. Gaskov A. M. Maso G. N. Layer-by-layer andysis of A,B thin-film hetero- structures using inductively coupled plasma atomic fluorescence spectrometry (ICP-AFS). Fresenius’ 9513790 9513791 9513792 9513793 9 513 794 9 513 79 5 9 513 79 6 9513797 9513798 9513799 9513800 9513801 9513802 95/3803 Journal of Analytical Atomic Spectrometry November 1995 Vol.10 J. Anal. Chem. 1994 349 424. (Chem. Dept. Moscow State Univ. Moscow 119899 Russia). Erber D. Bettmer J. Cammann K. Sensitive detection of ionic organolead compounds by coupling hydride generation (HG) with transversely heated graphite atomizer-atomic absorption spectrometry (THGA- AAS). Fresenius’ J. Anal. Chern. 1994 349 738. (Inst. Chem. Biosensorik eV Westfaelische Wilhelms Univ. D-48149 Munster Germany). Chakraborty R. Das A. K. Determination of vanadium by ETAAS using chromium nitrate as chemical modifier. Fresenius’ J. Anal. Chem. 1994 349 774. (Dept. Chem. Univ. Burdwan Burdwan 713 104 India). Gao Y.-g. Deng B. Studies on the atomization mechanism of elements on the graphite probe surface in the graphite furnace. XIV.Atomization mechanism of samarium. Gaodeng Xuexiao Huaxue Xuebao 1994 15 809. (Dept. Chem. Tsinghua Univ. Beijing 100084 China). Zhang B.4. Studies on cathode materials by cathodic sputtering in glow discharge atomic absorption spec- trometry having transient mode of atomization. Gaodeng Xuexiao Huaxue Xuebno 1994,15,997. (Dept. Chem. Hubei Univ. Wuhan 430062 China). Fei H. Tang B.-f. Determination of rare earth and non-rare earth impurities in gadolinia by ICP-AES. Hedongli Gongcheng 1994 15 357. (Nucl. Power Inst. China Chengdu 610005 China). Ma Y.-z. Zhu L. Li Z.-k. Wang J.-z. Bai J. Li Y.-q. Li B.-w. Zheng H. Determination of environ- mental cadmium by graphite furnace atomic absorption spectrometry using pyrolytic graphite tube and stan- dardless method. Huanjing Huaxue 1994 13 332.(China Natl. Centre Environ. Anal. and Measure. Beijing 100012 China). Mitra K. Roy U. S. Reversed phase extraction chromatographic studies of mercury (11) with high molecular weight carboxylic acid (Versatic- 10) and its analytical applications. Indian J. Chem. Sect. A Inorg. Bio-inorg. Phys. Theor. Anal. Chem. 1994 33 961. (Dept. Chem. Santiniketan 731 234 India). Wruck D. A. RUSSO R. E. Silva R. J. Thermal lens spectroscopy of plutonium using a laser diode and fibre optics. J. Alloys Compd. 1994 213 481. (Nucl. Chem. Div. Lawrence Livermore Natl. Lab. Livermore CA 94550 USA). Millier B. Sun X.-y. Aue W. A. Multichannel chromatography and on-line spectra from a flame photometric detector. J. Chrornatogr.A 1994,675 155. (Dept. Chem. Dalhousie Univ. Halifax Nova Scotia Canada B3H 453). Pedersen-Bjergaard S. Greibrokk T. N- 0- and P-selective on-column atomic emission detection in capillary gas chromatography. J. Chromatogr. A 1994 686 109. (Dept. Chem. Univ. Oslo P.O. Box 1033 Blindern 0315 Oslo Norway). Ahmad I. Goddard B. J. Overview of laser-induced breakdown spectroscopy. J. Fiz. Malays. 1993 14 43. (MIMOS Minist. Sci. Technol. and Environ. Kuala Lumpur 50490 Malaysia). Panwar 0. S. Mathur S. P. Determination of nickel(I1) by atomic absorption spectrometry by adsorption of its l-hydroxy-1,3-diphenyl-2-thiourea complex on micro- crystalline naphthalene. J. Indian Chem. SOC. 1994 71 219. (Res. Lab. Gov. Coll. Ajmer 305 001 India). Schniirer-Patschan C. Groll H.Zybin A. Niemax K. Application of diode lasers for analysis. J. Phys. I V 1994 4 639. (Inst. Spektrochem. Angew. Spektrosk. Dortmund Germany). Candelone J.-P. Bolshov M. A. Rundniev S. N. Hong S. Boutron C. F. Determination of bismuth down to subpg/g level in Greenland snow by laser excited9513804 9513805 9513806 9513807 9513808 9513809 9513810 951381 1 9513812 9513813 95/38 14 9513815 95/38 16 atomic fluorescence spectrometry. J. Phys. IV 1994 4 661. (Environ. CNRS Domaine Univ. 38402 St. Martin &Heres France). Chekalin N. V. Marunkov A. G. Vlasov I. I. Khalmanov A. T. Multipurpose atomic-ionization spec- trometer analysis of high-purity substances. Khim. Vys. Energ. 1994 28 465. (Inst. Geol. Anal. Khim. in V.I. vernadskogs Moscow Russia). Ohmori T. Yoshiike Y.Okamura S. Iwasaki I. Hanano R. Concentration by a microwave oven of trace elements in water and dissolution of elements from vessel. Kogyo Yosui 1994,433,22. (Fac. Sci. Toho Univ. Funabashi 274 Japan). Osojnik A. Drglin T. Comparison of graphite furnace and hydride generation AAS for trace analysis of tin in steels and nickel alloys. Kovine Zlitine Tehnol. 1993 27 301. (Inst. Kovinske Mater. Technol. Ljubljana Slovenia). Yang B.-g. Shi Y.-y. Molecular absorption spectro- metric determination of microamounts of fluoride by Mo-coated graphite tube. Lihua Jianyan Huaxue Fence 1994 30 74. (Hangzhou Iron Steel Works Hangzhou 310022 China). Szpunar-Lobinska J. Ceulemans M. Dirkx W. Witte C. Lobinski R. Adams F. C. Interferences in ultratrace speciation of organolead and organotin by gas chroma- tography with atomic spectrometric detection.Mikrochim. Acta 1994 113 287. (Dept. Chem. Univ. Antwerp B-2610 Antwerpen Belgium). Xu S.-k. Fang Z.4. Efficient flow injection on-line dilution system for flame atomic absorption spec- trometry based on micro-zone penetration. Microchem. J. 1994 50 145. (Flow Injection Anal. Res. Centre Inst. Appl. Ecol. Shenyang 10015 China). Darke S. A. Tyson J. F. Review of solid sample introduction for plasma spectrometry and a comparison of results for laser ablation electrothermal vaporization and slurry nebulization. Microchem. J. 1994 50 310. (Dept. Chem. Univ. Massachusetts Amherst MA Moenke-Blankenburg L. Kammel J. Schumann T. Microanalysis by laser ablation-inductively coupled plasma-atomic emission spectrometry in comparison to spark ablation of certified and found minerals galena sphalerite and pyrite.Microchem. J. 1994 50 374. (Dept. Chem. Inst. Anal. Environ. Chem. Martin- Luther Univ. Halle-Wittenberg D-06120 Halle Germany). Saitoh K. Sugiyama H. Struessmann C. A. Takashima F. Kawabata K. Determination of elements in sea water and somatic fluids of marine fish. Nippon Kaisui Gakkaishi 1994 48 248. (Akita Prefect. Inst. Fish. Fish. Manage. Oga 010-05 Japan). Nagahiro T. Katsuya U. Satake M. Column precon- centration of zinc using 4-( 2-pyridy1azo)resorcinol and the ion-pair materials of trioctylmethylammonium and bromate supported on biphenyl and its analysis using atomic absorption spectrometry. Orient. J. Chem. 1994 10 1. (Fac. Eng. Himeji Inst.Technol. Himeji 671-22 Japan). Mostafa M. A. Kabil M. A. Elimination of the interfering effects in the determination of cadmium by flame atomic absorption spectrophotometry. Proc. Pak. Acad. Sci. 1994 31 39. (Fac. Sci. Mansoura Univ. Mansoura Egypt). Duffey T. P. McNeela T. G. Mazumder J. Absorption spectroscopic measurement of atomic density in laser- induced vapour plume. Proc. SPIE-Int. SOC. Opt. Eng. 1994 2306 127. (Centre for Laser-Aided Mater. Process. Univ. Illinois Urbana IL 61801 USA). Eiras S. de P. Zamora P. G. P. Reis E. L. Effect of solvent mixtures in atomic absorption spectrophoto- 01003-4510 USA). 9513 8 17 95/38 18 9513819 9513820 9 513 82 1 9513822 9513823 9 513 824 95j3825 9513826 9 513 827 95/3828 9513829 9513830 9513831 metric determination. Quim.Nova 1994 17 369. (Dept. Quim. Univ. Federal Uberlandia 38400-902 Uberlandia Brazil). Williams D. T. Green A. E. S. New continuum-source atomic absorption spectrometer. Rev. Sci. Instrum. 1994 65 3339. (Clean Combust. Technol. Lab. Univ. Florida Gainesville FL 3261 1 USA). Sauke T. B. Becker J. F. Loewenstein M. Gutierrez T. D. Bratton C. G. Overview of isotopic analysis using tunable diode laser spectrometry. Spectroscopy (Eugene Oreg.) 1994 9 34. (Solar System Explor. Branch NASA Ames Res. Centre Moffett Field CA Gillette R. K. Preliminary studies of direct sequential analysis of varied composition solid alloys by multi- element atomic absorption. Spectroscopy (Eugene Oreg.) 1994 9 42. (Haynes Intl. Inc. Kokono IL Wagatsuma K. Hirokawa K. New spectrometric method for determination of sputtering parameters in glow discharge plasmas-use of helium matrix plasma gas.Surf. Interface Anal. 1994 21 631. (Inst. Mater. Res. Tohoku Univ. Sendai 980 Japan). Morlot M. Analytical aspects of lead in the environ- ment. Tech. Sci. Methodes Genie Urbain-Genie Rural 1994 2 79. (Lab. Hyg. et Rech. Sante Publique Vandoeuvre-les-Nancy France). Bayona J. M. Cai Y. Role of supercritical fluid extraction and chromatography in organotin speciation studies. Trends. Anal. Chem. 1994 13 327. (Barcelona Spain). Hu B. Jiang Z.-c. Zeng Y. Study on analyte transport process in fluorination-assisted electrothermal vapouriz- ation-inductively coupled plasma-atomic emission spec- trometry. Wuhan Daxue Xuebao Ziran Kexueban 1994 2 95. (Dept.Chem. Wuhan Univ. Wuhan 430072 China). Wang Y.-x. Hao J.-n. Review of determination of total aluminium in steel by FAAS and application of perchloric acid in FAAS. Yejin Fenxi 1994 14 35. (Central Iron and Steel Res. Inst. Beijing 100081 China). Chen G.-h. Determination of tungsten trioxide in tungsten concentrates by AAS. Yejin Fenxi 1994 14 50. (Zhuzhou Hard Alloy Co. Zhuzhou China). Zhang Y.-d. Zeng M. Lin G.-b. Han YA. Lai J. Xia Y.-m. Simultaneous direct determination of rare earth elements and part of non-rare earth elements in bastnaesite concentrates by ICP-AES. Yejin Fenxi 1994 14 53. (Ganjia Rare Earth Co. Ltd. 34110 China). Zolotovitskaya E. S. Glushkova L. V. Shtitel’man Z. V. Trubayeva T. N. Application of atomic emission spectral analysis for determining impurities of abundant elements in potassium dihydro- and dideuterophosphate single crystals. Zh.Prikl. Spektrosk. 1994 60 217. (Inst. Monokristall Kharkov 3 10001 Ukraine). Morozov V. N. Prokopchuk S. I. Comparative determi- nation of gold by emission and atomic absorption methods of scintillation analysis. Zavod. Lab. 1994 60(9) 16. (Russia). Stolyarova I. V. Orlova V. A. Autoclave treatment of samples in the analysis of compounds containing aluminium and silicon. Zh. Anal. Khim. 1994 49 817. (State Inst. Res. and Design Rare-Metal Ind. Moscow 109017 Russia). Ganeev A. A. Sholupov S. E. Maidurov A. D. Novel differential atomic absorption method for the isotopic analysis of mercury. Zh. Anal. Khim. 1994 49 830. (Inst. Chem. St. Petersburg State Univ. St.Petersburg 198904 Russia). Gergely S. Cakrt M. Testing of the flow injection technique with the sequential ICP-spectrometer 94035-1000 USA). 46904-9013 USA). Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 345 R9513832 9513833 9513834 9 513 83 5 9513836 9513 837 95/3 83 8 95/3839 95/3840 9513841 95/3842 9 513 843 95/3844 346 R 3510-ICP. Zh. Anal. Khim. 1994,49 1073. (Dept. Anal. Chem. Slovak Tech. Univ. Bratislava 8 1237 Slovakia). Feng X.-j. Shang L.-y. Determination of microamounts CaO and Mgo in high-purity bismuth trioxide by FAAS. Yejin Fenxi 1994 14 55. (Beijing Inst. Min. Metall. 100044 China). Baraj B. Cocoli V. Karayannis M. Robinson D. Experimental examination of the sodium potassium calcium strontium and magnesium effects in the AES determination of Li in the underground brines.ACH Models Chem. 1994 131 597. (Fac. Nat. Sci. Anal. Chem. Univ. Tirana Tirana Albania). Varga I. Arsenic determination in soils using continu- ous and flow-injection hydride generation ICP-AES. ACH Models Chem. 1994 131 661. (Dept. Inorg. and Anal. Chem. L. Eotvos Univ. Budapest Budapest 112 Hungary). Majcen N. Statistical approach to the development of a method for trace element determination in titanium@) oxide pigments by atomic absorption spectrometry. Anal. Methods Instrum. 1995 2 35. (Qual. Control Dept. Cinkarna Celje 63000 Celje Slovenia). Al-Khamis K. I. Al-Hadiyah B. M. Bawazir S. A. Ibrahim 0. M. Al-Yamani M. J. Quantification of muscle tissue magnesium and potassium using atomic absorption spectrometry.Anal. Lett. 1995 28 1033. (Dept. Clin. Pharm. King Saud Univ. Riyadh Saudi Arabia). Kagawa K. Hattori H. Ishikane M. Ueda M. Kurniawan H. Atomic emission spectrometric analysis of steel and glass using a TEA carbon dioxide laser- induced shock wave plasma. Anal. Chim. Acta 1995 299 393. (Fac. Educ. Fukui Univ. Fukui 910 Japan). De Carlo E. H. Pruszkowski E. Laser ablation ICP-MS determination of alkaline and rare earth elements in marine ferro-manganese deposits. At. Spectrosc. 1995 16 65. (Dept. Oceanogr. Sch. Ocean and Earth Sci. and Technol. Univ. Hawaii Honolulu HI 98822 USA). Anderau C. Fredeen K. J. Thomsen M. Yates D. A. Analysis of wear metals in oil by ICP AES. At. Spectrosc. 1995 16 79. (Perkin-Elmer Corp. Norwalk CT 06859 USA). Vinas P. Campillo N.Lopez Garcia I. Hernandez Cordoba M. Rapid procedures for cobalt and nickel determination in slurried food samples by electrother- mal atomic-absorption spectrometry. At. Spectrosc. 1995 16 86. (Dept. Anal. Chem. Univ. Murcia Marcia Spain). Tewari R. K. Gupta J. R. Determination of gold in geological materials by FAAS using potassium per- manganate and dilute hydrochloric acid at room temperature. At. Spectrosc. 1995 16 90. (Chem. Div. Geol. Surv. India Lucknow 226 020 India). Stuzka V. Soucek J. Determination of some nitrophe- nols by atomic absorption spectrometry (AAS) after extraction of ionic associates involving the bipyridylcop- per@) or phenanthrolinecopper(I1) complex. Collect. Czech. Chem. Commun. 1994 59 2227. (Dept. Anal. and Org. Chem. Palacky Univ.7712 46 Olomouc Czech Republic). Dennis M. J. Burrell A. Mathieson K. Willetts P. Massey R. C. Determination of the flour improver potassium bromate in bread by gas-chromatographic and ICP-MS methods. Food Addit. Contam. 1994 11 633. (Food Safety Directorate Food Sci. Lab. Minist. Agric. Fish and Food Colney Norwich UK NR4 7UQ). Yu H.-f. Wang A.-x. Jiang G.-h. Xu S.-k. Yang G.-q. Liquid membrane enrichment of trace copper cobalt nickel calcium and manganese in highly pure rare-earth oxide. Fenxi Shiyanshi 1995 14 56. (Changchun Normal Coll. Changchun 130032 China). 9513845 9513846 95/3847 9513848 95/3849 9513850 9513851 9513 8 52 9513853 9513 8 54 9513 8 5 5 9 513 8 56 9513 8 57 Lu S.-l. Li S.-z. Hao G.-z. Xu P.-z. Li J.-h. Liu Y. X-ray fluorescence spectrometric analysis of rare- earth elements.Fenxi Shiyanshi 1995,14,66. (Gen. Res. Inst. Non-ferrous Metals Beijing 100088 China). Walcerz M. Garbos S. Bulska E. Hulanicki A. Continuous flow hydride generation for the preconcen- tration and determination of arsenic and antimony by GFAAS. Fresenius’ J. Anal. Chem. 1994 350 662. (Dept. Chem. Univ. Warsaw PL-02-093 Warsaw Poland). Forsyth D. S. Hayward S. Further development and optimization of a quartz-tube atomizer for a gas chromatography-atomic absorption spectrometer system. Fresenius’ J. Anal. Chem. 1995,351,403. (Food Res. Div. Bur. Chem. Safety Food Dir. Health Prot. Branch Health Canada Ottawa Ontario Canada K1 OL2). Rubio J. A. R. Rauret R. G. Arsenic speciation in marine biological materials by LC-UV-HG-ICP/OES. Fresenius’ J.Anal. Chem. 1995 351 415. (Dept. Quim. Anal. Univ. Barcelona 08028 Barcelona Spain). Alberti J. Rubio R. Rauret G. Extractions method for arsenic speciation in maritime organisms. Fresenius’ J. Anal. Chem. 1995 351 420. (Dept. Quim. Anal. Univ. Barcelona 08028 Barcelona Spain). Cobo-Fernandez M. G. Palacios M. A. Chakraborti D. Quevauviller P. Camara C. On-line speciation of selenium(vr) selenium(1v) and trimethylselenium by HPLC-microwave oven-hydride generation-atomic absorption spectrometry. Fresenius’ J. Anal. Chem. 1995 351 438. (Dept. Quim. Anal. Fac. Ciencias Quim. Univ. Complutense 28040 Madrid Spain). Padro A. Rubio R. Rauret G. Germanium speciation by LC-HG ICP OES. Fresenius’ J. Anal. Chem. 1995 351 449. (Dept. Quim. Anal. Fac. Quim. Univ.Barcelona 08028 Barcelona Spain). Mena M. L. McLeod C. W. Jones P. Withers A. Minganti V. Capelli R. Quevauviller P. Microcolumn preconcentration and gas chroma tography-microwave induced plasma atomic emission spectrometry (GC-MIP-AES) for mercury speciation in waters. Fresenius’ J. Anal. Chem. 1995,351,456. (Environ. Res. Centre Div. Chem. Sch. Sci. Sheffield Hallam Univ. Sheffield UK S1 1WB). Johansson M. Emteborg H. Glad B. Reinholdsson F. Baxter D. C. Preliminary appraisal of a novel sampling and storage technique for the speciation analysis of lead and mercury in sea water. Fresenius’ J. Anal. Chem. 1995 351 461. (Dept. Anal. Chem. Umea Univ. 901 87 Umea Sweden). Craig P. J. Dewick R. J. van Elteren J. T. Use of sodium tetraethylborate for the analysis of trimethyllead species in artificial rain water and a natural road dust sample. Fresenius’ J.Anal. Chem. 1995,351,467. (Dept. Chem. De Montfort Univ. Leicester UK LE1 9BH). Minganti V. Capelli R. De Pellegrini R. Evaluation of different derivation methods for the multi-element detection of mercury lead and tin compounds by gas chromatography-microwave induced plasma atomic emission spectrometry in environmental samples. Fresenius’ J. Anal. Chem. 1995 351 471. (Inst. Anal. Technol. Farm. Alimentari Univ. Genova 16147 Genoa Italy). Schramel P. Wendler I. Molybdenum determination in human serum (plasma) by ICP-MS coupled to a graphite furnace. Fresenius’ J. Anal. Chem. 1995 351 567. (GSF-Res. Centre Environ. and Health Inst. Ecol. Chem. 85758 Oberschleissheim Germany).Edel H. Quick L. Cammann K. Frequency-modulated simultaneous multielement atomic absorption spec- trometry using electrothermal atomizer and deuterium background correction. Fresenius ’ J. Anal. Chem. 1995 351 479. (Inst. Chemo- und Biosensorik Westfalische Wilhelms Univ. 48149 Munster Germany). Journal of Analytical Atomic Spectrometry November 1995 Vol. 109513858 9513859 9513860 9513861 9513862 9513863 9513864 95/3865 9513866 9513867 9513868 95/3869 9513870 9513871 Herber R. F. M. Grobecker K. Collaborative study using solid sampling graphite furnace atomic absorption spectrometry. Fresenius’ J. Anal. Chem. 1995 351 577. (Coronel Lab. Occup. and Environ. Health Acad. Med. Centre Univ. Amsterdam 1105 Amsterdam Netherlands). Zheng J.-g. Zhang Z.-x. Monte Carlo technique for studying chemical and physical processes in ICP-AES.Guangpuxue Yu Guangpu Fenxi 1994 14(5) 43. (Dept. Chem. Zhongshan Univ. Guangzhou 5 10275 China). Tan S.-x. Cao L.-j. Li T.-r Determination of major elements in geological rock soil and deposit samples by inductively coupled plasma atomic emission spec- troscopy. Guangpuxue Yu Guangpu Fenxi 1994 14( 5) 38. (Centre Testing and Anal. Central South Univ. Technol. 410083 Changsha China). Yan Z. Sun H.-w. Zhang J.-s. Li Y.-x. Zhu B. Determination of copper in whole blood samples from the human ear by micro-sample-injection first-order- derivative flame AAS. Guangpuxue Yu Guangpu Fenxi 1994 14(5) 63. (Chem. Dept. Hebei Univ. Baoding 071002 China). Lei Z.-l. Zhang J.-y. Ren Y. Yu Z.-b. Gan S.-c.Liu C.-j. Determination of trace gold in ore by rapid preconcentration with polyurethane foam and graphite- furnace atomic absorption spectrophotometry. Guangpuxue Yu Guangpu Fenxi 1994 14(5) 73. (Changchun Inst. Appl. Chem. Acad. Sin. Changchun 130022 China). Ma Y.-p. Zhan G.-l. Han Y.-q. Study of the direct analysis of solid samples by graphite furnace AAS. 11. Determination of cadmium. Guangpuxue Yu Guangpu Fenxi 1994 14(5) 79. (Anal. and Testing Centre Xin Jiang Urumqi 830011 China). Zhang M.-y. Chen W.-j. Determination of iron and manganese in soya bean tea and alloys by flame AAS. Guangpuxue Yu Guangpu Fenxi 1994 14( 5) 85. (Dept. Chem. Suzhou Univ. Suzhou 215005 China). Liu H.-w. Peng X.-k. Bao L.-s. Pan Z.-g. Feng J.4. Determination of aluminium in beer by GFAAS.Guangpuxue Yu Guangpu Fenxi 1994,14( 5) 89. (Hunan Prov. Health and Anti-epidemic Station Changsha 410005 China). Yu D.-k. Determination of vanadium and nickel in rock extracts by X-ray fluorescence spectrometry by the formed-filter-paper method. Guangpuxue Yu Guangpu Fenxi 1994 14(5) 91. (Lanzhou Inst. Geol. Acad. Sin. Lanzhou 73000 China). Browner R. F. Sample introduction for plasma spectro- chemistry and mass spectrometry 1974-1994 personal recollections on the twentieth anniversary of the ICP Information Newsletter. ICP In$ Newsl. 1994 20 25 1. (Sch. Chem. and Biochem. Georgia Inst. Technol. Atlanta GA 30332-0400 USA). Gillyon E. C. P. Hunter J. Tye C. T. Alavosus T. Improving ICP and ICP-MS instrument up-time and reducing service costs by use of a remote diagnostic facility.Int. Labmate 1994 19 33. Anderson D. L. Cunningham W. C. Lindstrom T. R. Olmez I. Identification of lead and other elements in ceramic glazes and housewares by cadmium- 109- induced X-ray fluorescence emission spectrometry. J. AOAC Int. 1995 78 407. (Centre Food Safety and Appl. Nutr. Elemental Res. Branch US Food and Drug Admin. Washington DC 20204 USA). Qian S.-h. Huang G.-q. Sun Y.-c. Graphite furnace AAS determination of traces of germanium in glossy Ganoderma drinks. Lihua Jianyan Huaxue Fence 1995 31 37. (Dept. Environ. Sci. Wuhan Univ. Wuhan 430072 China). He Z.-p. Chen L.-z. Liu M.-h. Hydride-generation AAS determination of mercury in water using a self- 9513872 9513873 9 513 874 9513875 9513876 9 513 877 95/3878 9 513 879 9513880 9513881 9513882 951388 3 9513884 made T-shape quartz tube.Lihua Jianyan Huaxue Fence 1995,31 40. (Sanitation and Anti-epidemic unit Air Force Logistics Bur. Beijing 100076 China). Shi C.-h. Gao S.-b. Gong S.-m. Ji Z.-t. Pulse sampling flame AAS determination of combined and uncombined zinc in blood serum. Lihua Jianyan Huaxue Fence 1995 31 41. (Dept. Military Hyg. Fourth Univ. Military Med. Sci. Xi’an 710032 China). Guan X.-j. Li D.-f. Mo D.4. On the simultaneousness between the adjustment of the grating position and the wavelength indication-experience on the maintenance of the JY 38 ICP spectrometer. Lihua Jianyan Huaxue Fence 1995 31 44. (Guangxi Res. Centre Anal. and Testing Nanchang 530022 China). Leng J. Extraction and flame AAS determination of micro amounts of copper zinc iron and manganese in water. Lihua Jianyan Huaxue Fence 1995 31 48.(Hemps Res. Inst. Chinese Acad. Agric. Sci. Yuanjiang 413100 Hunan China). Mogg M. Rudolf J. Microwave-or classical diges- tion? LaborPraxis 1994 18 22. (Lab. Heppeler 79537 Loerrach Germany). Knipping B. Siemann M. G. Herrmann K. Analysis of soil samples and waste by X-ray fluorescence and X-ray diffraction. LaborPraxis 1994 18 78. (Inst. Mineral. and Mineralische Rohstoffe 38678 Clausthal- Zellerfeld Germany). Wheeler R. M. Chaturvedi R. P. Duggan J. L. Marble D. K. Braswell D. Trace-element analysis of steel samples with synchrotron radiation. Nucl. Instrum. Methods Phys. Res. Sect. B 1993,79 545. (Dept. Phys. SUNY Coll. Cortland NY 13045 USA). D’ Anna A. D’ Alessio A.Minutolo P. Spectroscopic and chemical characterization of soot inception pro- cesses in premixed laminar flames at atmospheric pressure. Springer Ser. Chem. Phys. 1994 59 83. (Inst. Ric. sulla Combustione CNR 1-80125 Naples Italy). Gilmutdinov A. Kh. Radziuk B. Sperling M. Welz B. Nagulin K. Yu. Spatial distribution of radiant intensity from primary sources for atomic absorption spectrometry. Part I. Hollow cathode lamps. Appl. Spectrosc. 1995 49 413. (Dept. Appl. Res. Bodenseewerk Perkin-Elmer GmbH D-88647 Uberlingen Germany). Sabsabi M. Cielo P. Quantitative analysis of alu- minium alloys by laser-induced breakdown spec- troscopy and plasma characterization. Appl. Spectrosc. 1995 49 499. (Ind. Mater. Inst. Natl. Res. Council Canada 75 De Mortagne Blvd. Boucherville Quebec Canada J4B 6Y4).Pereiro R. Starn T. K. Hieftje G. M. Gas-sampling glow discharge for optical emission spectrometry. Part 11. Optimization and evaluation for the determination of nonmetals in gas-phase samples. Appl. Spectrosc. 1995 49 616. (Dept. Chem. Indiana Univ. Bloomington IN 47405 USA). Petrucci G. A. Imbroisi D. Guenard R. D. Smith B. W. Winefordner J. D. High-spatial-resolution OH rotational temperature measurements in an atmos- pheric-pressure flame using an indium-based resonance ionization detector. Appl. Spectrosc. 1995 49 655. (Dept. Chem. Univ. Florida Gainesville FL 3261 1 USA). Yang P. Myers D. P. Li G. Hieftje G. M. Constant- fraction discrimination/boxcar integrator for plasma source time-of-flight mass spectrometry. Appl. Spectrosc.1995 49 660. (Dept. Chem. Indiana Umv. Bloomington IN 47405 USA). Ali A. H. Comparison of microwave-assisted digestion methods for the analysis of hydrotreating catalysts by atomic emission. Appl. Spectrosc. 1995,49,682. (Texaco R&D P.O. Box 1608 Port Arthur TX 77641 USA). Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 347 R9513885 9513886 9513 887 95/3888 9513889 9513890 9513891 9513892 9513893 9513894 9513 895 9 513 8 96 95/3897 9513898 348R Repasky K. S. Watson L. E. Carlsten J. L. High- finesse interferometers. Appl. Opt. 1995,34,2615. (Dept. Phys. Montana State University Bozeman MN 59717 USA). Flanigan D. F. Discrepancies between two formulations of signal-to-noise ratio for background-limited detec- tion. Appl. Opt. 1995 34 2721.(Dev. and Eng. Center US Army Edgewood Res. Aberdeen Proving Ground MD 21010-5423 USA). Whitehead C.-A. Cannon B. D. Wacker J. F. Trace detection of krypton using laser-induced fluorescence. Appl. Opt. 1995 34 3250. (Pacific Northwest Lab. Richland WA 99352 USA). Thumann A. Seeger T. Leipertz A. Evaluation of two different gas temperatures and their volumetric fraction from broadband N coherent anti-Stokes Raman spec- troscopy spectra. Appl. Opt. 1995 34 3313. (Lehrstuhl Tech. Thermodynamik Univ. Erlangen-Nurnberg Am Weichselgarten 8 D-91058 Erlangen Germany). McNesby K. L. Daniel R. G. Morris J. B. Miziolek A. W. Tomographic analysis of CO absorption in a low-pressure flame. Appl. Opt. 1995 34 3318. (US Army Res. Lab. US Army Aberdeen Proving Ground Colodner D.Salters V. Duckworth D. C. Ion sources for analysis of inorganic solids and liquids by MS. Anal. Chem. 1994 66 1079A. (Lamont-Doherty Earth Observatory Columbia Univ. Morningside Heights New York NY 10027 USA). Tu Q. Shan X.-q. Jin Q. Ni Z.-m. Trace metal redistribution during extraction of model soils by acetic acidlsodium acetate. Anal. Chem. 1994 66 3562. (Res. Centre Eco-Environ. Sci. Acad. Sin. P.O. Box 2871 Beijing 100085 China). MD 21005-50066 USA). Mansoori B. A. Johnston M. V. Wexler A. S. Quantitation of ionic species in single microdroplets by on-line laser desorption/ionization. Anal. Chem. 1994 66 3681. (Depts. Chem. and Biochem. and Mech. Eng. Univ. Delaware Newark DE 19716 IJSA). Stafilov T. Rizova V. Determination of chromium in cereals by electrothermal atomic absorption spec- trometry.Acta Pharm. (Zagreb) 1994 44 97. (Fac. Sci. Univ. St. Kiril 91000 Skopje Yugoslavia). Bauer W. F. Micca P. L. White B. M. Rapid method for the direct analysis of boron in whole blood by atomic emission spectroscopy. Adv. Neutron Capture Ther. [Proc. Int. Symp.] 5th 1992 1993 403. (Idaho Natl. Eng. Lab. EG and G Idaho Inc. Idaho Falls ID 83402 USA). Hotz N. J. Bauer W. F. Determination of strongly protein-bound borocaptate species by high-performance liquid chromatography with online inductively coupled plasma atomic emission spectroscopy detection of boron. Adv. Neutron Capture Ther. [I'roc. Int. Symp.] 5th 2992 1993 439. (Idaho Natl. Eng. Lab. EG and G Idaho Inc. Idaho Falls ID 83415 USA). Shalmi M. Kibble J. Day J. P.Christensen P. Atherton J. C. Improved analysis of picomole quantities of lithium sodium and potassium in biological fluids. Am. J. Physiol. 1994 267 F695. (Dept. Pharm. and Med. Physiol. Univ. Copenhagen Copenhagen DK 2200 Denmark). Lopez Molinero A. Barriovero O. Lechon J. M. Castillo J. R. Determination of tellurium by generation and introduction of its hydride in low-power inductively coupled plasmas. An. Quim. 1993,89 597. (Fac. Cienc. Univ. Zaragoza,'Zaragoza 50009 Spain). Wielgus-Serafiaska E. Pawlicki K. Kaminski M. Circadian changes in Mg-dependent ATPase PAS reaction and magnesium content in the rat liver in relation to the age of rats and the season of year Ann. Acad. Med. Silesiensis 1992 14 105. (Second Dept. Journal of Analytical Atomic Spectrometry Novembe r .9513899 9513900 9513901 9513902 9513903 9 513 9 04 9513905 95/3906 9513907 9513908 9513909 9513910 951391 1 1995 VOl. 10 Histol. and Embryol. Silesian Sch. Med. 40-952 Katowice Poland). Fuentealba I. C. Bratton G. R. Role of the liver kidney and duodenum in tolerance in the copper- loaded rat. Anal. Cell. Pathol. 1994 6 345. (Coll. Vet. Med. Texas A and M Univ. College Station TX 77843 USA). Romero Rodriguez M. A. Lopez Hernandez J. Vazquez Oderiz M. L. Simal Lozano J. Mineral elements in various fruits. I. Calcium magnesium sodium and potassium. An. Bromatol. 1994 44 113. (Fac. Farm. Univ. de Santiago de Compostela Santiago de Compostela E-15706 Spain). Romero Rodriguez M. A. Lopez Hernandez J. Vazquez Oderiz M. L. Simal Lozano J. Mineral elements in various fruits.11. Iron copper zinc and manganese. An. Bromatol. 1994,44 119. (Fac. Farm. Univ. de Santiago de Compostela Santiago de Compostela E-15706 Spain). Ferreira I. M. P. L. V. O. Lima J. L. F. C. Rangel A. 0. S. S. Flow injection sequential determination of chloride by potentiometry and sodium by flame emis- sion spectrometry in instant soups. Anal. Sci. 1994 10 801. (Dept. Quim.-Fis. Fac. Farm. CEQUP Porto 4000 Portugal). Mueller B. Mebarek D. S tyrene-maleic acid copolymer as corrosion inhibitor for aluminum pigment in aqueous media. Angew. Makromol. Chem. 1994 221 177. (Fachbereich Farbe-Lack-Kunststoff Fachhochsch. Druck Stuttgart 0-70569 Stuttgart Germany). Millart H. Kantelip J. P. Platonoff N. Descous I. Trenque T. Lamiable D. Choisy H. Increased iron content in rat myocardium after 5-fluorouracil chronic administration.Anticancer Res. 1993 13 779. (Lab. Pharmacol. Med. Fac. Med. 51095 France). Ceulemans M. Witte C. Lobinski R. Adams F. C. Simplified sample preparation for GC speciation analy- sis of organotin in marine biomaterials. A p ~ l . Organomet. Chem. 1994 8 451. (Dept. Chem. Univ. Antwerp B-2610 Wilrijk Belgium). Koirtyohann S. R. Yates D. A. Determination of major minor and trace elements in NIST biological reference materials. At. Spectrosc. 1994 15 167. (Dept. Chem. Univ. Missouri Columbia MO USA). Lee J. Treloar B. P. Grace N. D. Metallothionein and trace element metabolism in sheep tissues in response to high and sustained zinc dosages. 11. Expression of metallothionein m-RNA. Aust. J.Agric. Res. 1994 45 321. (Grasslands Res. Centre AgRes. Palmerston North New Zealand). Falandysz J. Kotecka W. Bona H. Manganese copper zinc and iron content of edible tubers roots root-stocks fruits and seeds of vegetables cultivated in the province of Gdansk and Elblag. Bromatol. Chem. Toksykol. 1993,26,97. (Z. Zespolu Naukowego Chemii i Toksykologii Srodowiska Wydzialu Chem. Univ. Gdanskiego Gdansk Poland). Falandysz J. Kotecka W. Bona H. Manganese copper zinc and iron content of leafy vegetables cultivated in the province of Gdansk. Bromatol. Chem. Toksykol. 1993 26 101. (Z. Zespolu Naukowego Chemii i Toksykologii Srodowiska Wydzialu Chemii Univ. Gdanskogo Gdansk Poland). Zhang J.-s. Wang Y.-m. Shi Y. Wang B.-z. Bu F.-q. Liu. J.-y. Study on contents of trace elements Sr Ni Se4+ in different parts of Jilin panax ginseng.Baiqiuen Yike Dame Xuebao 1994 20 109. (Inst. Endemic Dis. Norman Bethune Univ. Med. Sci. Changchung China). Isegawa J. Matsuda A Yamamoto K. Kumamoto T. Terashima K. Kataoka M. Sato M. Selenium concentrations and glutathione peroxidase activities of9513912 95/39 13 9513914 95/39 15 9513916 95/39 17 95/39 18 9513919 9513920 9513921 9513922 9513923 9513924 plasma erythrocytes and platelets in healthy adult volunteers. Biomed. Res. Trace Elem. 1993 4 75. (Res. Lab. Roussel Morishita Co. Ltd. Yasugi 520-23 Japan). Itoh N. Morinaga N. Kouzai T. Purification and characterization of a novel metal-containing nonheme bromoperoxidase from Pseudomonas putida. Biochim. Biophys. Acta 1994 1207 208. (Dept.Appl. Chem. and Biotechnol. Fac. Eng. Fukui Univ. Bunkyo 3-9-1 Fukui 910 Japan). Kotulan J. Totusek J. Sefflova A Polach J. Lead in bone from south Moravian autopsies. Cent. Eur. J. Public Health 1994 2 42. (Fac. Med. Masaryk Univ. Brno Czech Republic). Johansson C. G. Determination of aluminium in beer by GF-AAS. Cereuisia Biotechnol. 1994 19 40. (UK). Treiber G. Walker S. Klotz U. Omeprazole-induced increase in the absorption of bismuth from tripotassium dicitratobismuthate. Clin. Pharmacol. Ther. (St. Louis) 1994 55 486. (Robert Bosch Foundation 70376 Stuttgart Germany). Li Y.-m. Stanislavova L. Chaney R. L. Determination of total cadmium in calcareous soils by extraction using Aliquat-336 and 3-heptanone after aqua regia digestion. Commun. Soil Sci. Plant Anal.1994 25 2029. (Dept. Crop Weed Sci. N. Dakota State Univ. Fargo ND 58105 USA). Takahashi I. Maehara Y. Kusumoto H. Kohnoe S. Sugimachi K. Heat enhances the cytotoxicity of cis-diamminedichloroplatinum(II) and its analogs cis- 1,l -cyclobutanedicarboxylato (2R)-Zmethyl- 1,4-but- anediammineplatinum(11 and cis-diammine(glyco1ato)- platinum in uitro. Cancer Chemother. Pharmacol. 1993 33 31. (Fac. Med. Kyushu Univ. Higashi 812 Japan). Petros W. P. Chaney S. G. Smith D. C. Fangmeier J. Sakata M. Brown T. D. Trump D. L. Pharmacokinetic and biotransformation studies of ormaplatin in conjunction with a phase I clinical trial. Cancer Chemother. Pharmacol. 1994 33 347. (Compr. Cancer Centre Duke Univ. Med. Centre Durham NC 27710 USA). Arnaud J. Faure H. Bourlard P. Denis B.Favier A. E. Longitudinal changes in serum zinc concentration and distribution after acute myocardial infarction. Clin. Chim. Acta 1994 230 147. (Lab. Biochim. C. CHUG BP 217 38043 Grenoble France). Willuhn J. Schmitt-Wrede H. P. Greven H. Wunderlich F. Cadmium-induced mRNA encoding a non-metallothionein 33-kDa protein in Enchytraeus buchholzi (Oligochaeta). Ecotoxicol. Enuiron. Sa. 1994 29 93. (Math.-Nat. Fac. Heinrich-Heine-Univ. Dusseldorf 4000 Dusseldorf Germany). Udagama-Randeniya P. Savidge R. Electrophoretic analysis of coniferyl alcohol oxidase and related laccases. Electrophoresis ( Weinheim Fed. Rep. Ger.) 1994 15 1072. (Fac. For. Environ. Manage. Univ. New Brunswick Fredericton New Brunswick Canada E3B 6C2). Saellsten G. Barregaard L. Wikkelsoe C. Schuetz A.Mercury and proteins in cerebrospinal fluid in subjects exposed to mercury vapour. Enuiron. Res. 1994 65 195. (Dept. Occup. Med. Sahlgren’s Univ. Hosp. S-412 66 Goteborg Sweden). Ihnat M. Dabeka R. W. Wolynetz M. S. Preparation and homogeneity characterization of ten agricultural/ food reference materials for elemental composition. Fresenius’ J. Anal. Chem. 1994 348 445. (Centre Land Biol. Resour. Res. Agric. Canada Ottawa Ontario Canada K1A OC6). Fuchslueger U. Grether H.-J. Grasserbauer M. Hyphenation of Curie-point-pyrolysis high-resolution gas chromatography with several spectroscopic methods for the analysis of cured epoxy resins. Fresenius’ J. Anal. 9513925 9513926 9513927 9513928 9513929 9513930 9513931 9513932 9513933 9513934 9513935 9513936 9513937 9513938 9 513 9 3 9 Chem.1994 349 283. (Polymers Div. Ciba Geigy AG CH-4002 Basel Switzerland). Forsyth D. S. Sun W. F. Dalglish K. Survey of organotin compounds in blended wines. Food Addit. Contam. 1994 11 343. (Bur. Chem. Safety Health Canada Ottawa Ontario Canada K1A OL2). Coni E. Caroli S. Ianni D. Bocca A. Methodological approach to the assessment of trace elements in milk and dairy products. Food Chem. 1994 50 203. (1st. Super. Sanita 00161 Rome Italy). Liu Y.-x. Wu L.-m. Xie W.-j. Effect of sodium benzoate on the nucleation of poly(ethy1ene terephthal- ate) crystallization. Gaofenzi Cailiao Kexue Yu Gongcheng 1993 9 93. (Inst. Polym. Sci. Zhongshan Univ. Guangzhou China). Liu G.-s. Wang J.-y. Wang H. Han Z.-x. Determination of total water-soluble sugar in fruits and vegetables by indirect atomic absorption method.Hebei Daxue Xuebao Ziran Kuxueban 1994 14 72. (Shijiazhuang Inst. Agric. Modernization Chin. Acad. Sci. 050021 China). Huang A.-h. Wang X.-p. Sun H. Assaying perilym- phatic calcium in the rats’ cochlea by microsampling atomic absorption spectroscopy. Hunan Yike Daxue Xuebao 1994 19 264. (Dept. Environ. Med. Hunan Med. Univ. Changsha China). Hayes C. Curran P. M. T. Hynes M. J. Preservative leaching from softwoods submerged in Irish coastal water as measured by atomic absorption spectrophoto- metry. Holzforschung 1994 48 463. (Dept. Bot. Univ. Coll. Galway Galway Ireland). Lei X.-f. Wang L. Xing Q. Study of the genotoxicity and concentration of five metals in airborne particles. Huanjing Kexue 1993,14,30.(Dept. Epidemiol. Beijing Med. Univ. Beijing 100083 China). Ephraim J. H. Mathuthu A. S. Marinsky J. A. Calcium binding by fulvic acids studied by an ion selective electrode and an ultrafiltration method Humic Subst. Global Enuiron. Implic. Hum. Health Proc. Int. Meet. Int. Humic Subst. SOC. 6th 1992. Elsevier Amsterdam Netherlands 1994. 1125-30. Stobbaerts R. Robberecht H. Haesen F. Deelstra H. Manganese content of European wines. Int. J. Vitam. Nutr. Res. 1994 64 233. (Dept. Pharm. Sci. Univ. Antwerpen B-2610 Wilrijk Belgium). Adeyeye E. I. Determination of trace heavy metals in Illisha africana fish and in associated water and soil sediments from some fish ponds. Int. J. Enuiron. Stud. 1994 45 231. (Dept. Chem. Ondo State Coll. Educ. Ikere-Ekiti Nigeria).Yamane T. Determination of metal traces in plastics. ldemitsu Giho 1993,36,750. (Polym. Res. Lab. Idemitsu Petrochem. Co. Ltd. Ichihara 299-01 Japan). Benitez M. A. Grijalva M. I. Valencia M. E. Total and soluble iron content and effect of certain inhibitors present in selected varieties of tepary bean (Phaseolus Acutifolius). J. Agric. Food Chem. 1994 42 1300. (Centro Invest. Alim. Desarrollo Sonora Mexico). Cai X.-j. Uden P. C. Block E. Zhang X. Quimby B. D. Sullivan J. J. Allium chemistry identification of natural abundance organoselenium volatiles from garlic elephant garlic onion and Chinese chive using head- space gas chromatography with atomic emission detec- tion. J. Agric. Food Chem. 1994,42,2081. (Dept. Chem. Univ. Massachusetts Amherst MA 01003 USA).Quigley M. N. Determination of calcium in analgesic tablets using atomic absorption spectrophotometry. J. Chem. Educ. 1994 71 800. (Duquesne Univ. Pittsburgh PA 15282 USA). Hollingworth T. A Hungerford J. M. Barnett J. D. Wekell M. M. Total volatile acids temperature depen- Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 349 R9513940 95 f3941 9513942 9513943 9513944 9513945 9513946 9513947 9513948 9513949 9513950 9513951 350 R dent decomposition indicator in halibut determined by flow injection analysis. J. Food Prot. 1994 57 505. (Seafood Prod. Res. Centre US Food and Drug Admin. Bothell WA 98021-4421 USA). Schmid H. A. Requintina P. J. Oxenkrug G. F. Sturner W. Calcium calcification and melatonin biosynthesis in the human pineal gland a postmortem study into age-related factors. J.Pineal Res. 1994 16 178. (Pineal Res. Lab. VA Medical Center Providence RI USA). Barton J. C. Patton M. A. Edwards C. Q. Griffen L. M. Kushner J. P. Meeks R. G. Leggett R. W. Blood lead concentrations in hereditary hemochrom- atosis. J. Lab. Clin. Med. 1994 124 393. (Dept. Med. Veterans Admin. Med. Centre Birmingham AL 35209 USA). Prohaska J. R. Bailey W. R. Regional specificity in alterations of rat brain copper and catecholamines following perinatal copper deficiency. J. Neurochem. 1994 63 1551. (Sch. Med. Univ. Minnesota Duluth MN USA). Chary-Valckenaere I. Fener P. Jouzeau J.-Y. Netter P. Payan E. Floquet J. Burnel D. Kessler M. Pourel J. et al. Experimental articular toxicity of aluminium compounds in vivo. J.Rhemmatol. 1994 21 1542. (Dept. Rheumatol. Pharmacol. Nephrol. and Pathol. Univ. de Nancy I Vandoeuvre-les-Nancy France). Lim C. K. Lau C. H. Determination of total aluminium iron and silicon in soils under rubber by acid dissolution technique. J. Nut. Rubber Res. 1993 8 213. (Rubber Res. Inst. Malaysia Kuala Lumpur 50908 Malaysia). Cabrera C. Gallego C. Lopez M. C. Lorenzo M. L. Lillo E. Determination of levels of lead contamination in food and feed crops. J. AOAC Int. 1994 77 1249. (Sch. Pharm. Univ. Granada Granada E-18012 Spain). Deruaz D. Soussan-Marchal F. Joseph I. Desage M. Bannier A. Brazier J. L. Analytical strategy by coupling headspace gas chromatography atomic emis- sion spectrometric detection and mass spectrometry. Application to sulfur compounds from garlic.J. Chromatogr. A 1994 677 345. (Lab. &Etudes Anal. et Cien. du Med. Inst. Sci. Pharm. et Biol. 8 Ave. Rockfeller 69393 Lyon France). Carro-Diaz A. M. Lorenzo-Ferreira R. A. Cela- Torrijos R. Speciation of organomercurials in biological and environmental samples by gas chromatography with microwave-induced plasma atomic emission detec- tion. J. Chromatogr. A 1994 683 245. (Dept. Anal. Chem. Nutr. and Food Sci. Univ. Santiago de Compostela Avda. de las Ciencias s/n Santiago de Compostela (La Coruna) 15706 Spain). Tutschku S. Mothes S. Dittrich K. Determination and speciation of organotin compounds by gas chroma- tography-microwave induced plasma atomic emission spectrometry. J. Chromatogr. A 1994 683 269. (Dept. Anal. Chem. Centre for Environ. Res.Permoserstr. 15 043 18 Leipzig Germany). Meyer A. Schwedt G. Coupling of microwave ashing and hydride atomic absorption spectroscopy (AAS). LaborPraxis 1993 17(4) 44. (Abt. 1 Prozess- Umweltanal. Clausthaler Umwelttech. Inst. GmbH W-3392 Clausthal-Zellerfeld Germany). Kefalas V. Stacey N. H. Cellular K'. Methods Toxicol. 1994 lB 50. (Chem. Assess. Branch Univ. Sydney Sydney 2001 Australia). Asahina H. Kuraoka I. Shirakawa M. Morita E. H. Miura N. Miyamoto I. Ohtsuka E. Okada Y. Tanaka K. XPA protein is a zinc metalloprotein with an ability to recognize various kinds of DNA damage. Mutat. Res. 1994 315 229. (Inst. Mol. and Cell. Biol. Suita Osaka 565 Japan). 9513952 951395 3 9513954 9513955 9513956 95 f 3957 9513958 9513959 9513960 9513961 9513962 9513963 9513964 9513965 9513966 Journal of Analytical Atomic Spectrometry November 1995 Vol.10 Zhang J.-s. Wang Y.-m. Song X.-h. Sun L.-x. Sun Y.-z. Comparison of mineral element contents among different types of ginseng using inductively coupled plasma-atomic emission spectroscopy. Microchem. J. 1994 50 131. (N. Bethune Univ. of Med. Sci. Changchun 130021 China). Csikkel-Szolnoki A. Kiss S. A. Veres S. Elemental analysis of tea leaves by atomic spectroscopic methods. Magnesium Res. 1994 7 73. (Dept. Inorg. and Anal. Chem. Attila Jozsef Univ. H-6701 Szeged Hungary). Tanaka T. Aoki Y. Imou M. Okayama A. Oobayashi H. Sasaki M. Simple and rapid measure- ments of sodium potassium calcium magnesium and zinc in cow milk. Nara-ken Eisei Kenkyusho Nenpo 1993 27 137. (Nara Prefect. Inst. Public Health Nara 630 Japan).Berlet H. H. Bischoff H. Weinhardt F. Divalent metals of myelin and their differential binding by myelin basic protein of bovine central nervous system. Neurosci. Lett. 1994 179 75. (Inst. Pathochem. and Gen. Neurochem. Univ. Heidelberg Im Neuenheimer Feld 220-221 D-69120 Heidelberg Germany). Ng Y.-w. Snitch P. Pamphlett R. Spinal cord uptake of lead injected into muscle. Neurotoxicology 1994 15 315. (Dept. Pathol. Univ. Sydney Sydney NSW 2006 Australia). Otoguro C. Kaneko K. Hihara M. Odake S. Maeda Y. Changes in the characteristic properties of egg shell during ashing process and its effect on hardness of brined ume fruit. Nippon Shokuhin Kogyo Gakkaishi 1994 41 639. (Yamanashi Ind. Technol. Centre Kofu 400 Japan). Madamba L. S. P.Pamulaklakin M. A. Heavy metals in selected fish species collected from Laguna de Bay. Philipp. J. Sci. 1994 123 135. (Inst. Chem. Univ. Philippines Los Banos Philippines). Kalac P. Staskova I. Heavy metals in fruiting bodies of wild growing mushrooms of the genus Agaricus. Sb. UVTIZ Potravin. Vedy 1994 12 185. (Zemedelska Fak. Jihoceske Univ. 370 05 Czech Republic). Susin S. Abian J. Peleato M. L. Sanchez-Baeza F. Abadia A. Gelpi E. Abadia J. Flavin excretion from roots of iron-deficient sugar beet (Beta vulgaris L.). Planta 1994 193 514. (Dept. Plant Nutr. CSIC Zaragoza E-50080 Spain). Baldini M. Conti M. E. Molinaro M. G. Stacchini P. Zanasi F. Presence of lead in Italian wine evaluation of actual concentration. Riv. Sci. Aliment. 1993 22 429. (1st. Super. Sanita Rome Italy).Richelle-Maurer E. Degoudenne Y. Van de Vyver G. Dejonghe L. Some aspects of heavy metal tolerance in freshwater sponges Sponges Time Space Proc. Int. Porijiera Congr. 4th 1993. Balkema Rotterdam Netherlands 1994. 351. Altura B. T. Altura B. M. Method for distinguishing ionized complexed and protein-bound Mg in normal and diseased subjects. Scand. J. Clin. Lab. Invest. Suppl. 1994 54 83. (Depts. Physiol. and Med. State Univ. New York Brooklyn NY 11203 USA). Xiang L-r. Liu P.-h. Zhang B. Graphite furnace atomic absorption spectrometric determination of mic- roamounts of cobalt. Sichuan Daxue Xuebao Ziran Kexueban 1993 30 515. (Dept. Chem. Sichuan Univ. Chengdu China). Yamamura Y. Yoshinaga Y. Arai F. Kishimoto T. Background levels of total mercury concentrations in blood and urine.Sangyo Igaku 1994 36 66. (Dept. Public Health St. Marianna Univ. Sch. Med. Kawasaki 216 Japan). Slavin W. Graphite-furnace AAS. Tech. Instrum. Anal. Chem. 1994 15 53. (Bonaire Technol. Ridgefield CT 06877 USA).9513967 9513968 9513969 9513970 9513971 9513972 9513973 9513974 9513975 9513976 95/3977 9513978 9513979 9.513980 951398 1 Salvin W. Flame atomic absorption spectrometry. Tech. Instrum. Anal. Chem. 1994 15 87. (Bonaire Technol. Ridgefield CT 06877 USA). Schramel P. Atomic emission spectrometry. Tech. Instrum. Anal. Chem. 1994 15 91. (Inst. Oekolog. Chem. GSF-Forschungszentrum Umwelt und Gesundheit D-8042 Neuherberg Germany). Dang D.-n. Vo VA. Nguyen K.-v. Nguyen D.4. Sample preparation procedure for the determination of "N isotope abundance using emission spectrometry.Tap Chi Hoa Hoe 1994 32 67. (Inst. Nucl. Sci. Technique Vietnam Natl. At. Energy Comm. Vietnam). Henry R. B. Liu J. Choudhuri S. Klaassen C. D. Species variation in hepatic metallothionein. Toxicol. Lett. 1994 74 25. (Dept. Pharmacol. Toxicol. and Ther. Environ. and Occup. Health Center Univ. Kansas Med. Center Kansas City KS 66160-7417 USA). Sehnke P. C. Johnson J. E. Chromatographic analysis of capsid protein isolated from alfalfa mosaic virus zinc binding and proteolysis cause distinct charge heterogeneity. Virology 1994 204 843. (Interdisciplin. Center Biotechnol. Res. Univ. Florida Gainesville FL 32611 USA). Cherubin S. Buiatti S. Battistutta F. Zironi R. Use of neocuproine for the colorimetric determination of copper in wine.Wein-Wiss. 1994 49 78. (Dept. Food Sci. Univ. Udine 1-33100 Udine Italy). Su Y. Gao J.-q. Wang H-z. Determination of the heavy metals in the Chinese total diet study. Weisheng Yanjiu 1993,22,55. (Inst. Nutr. and Food Hyg. Chinese Acad. Preventive Med. Beijing 100050 China). Ma Y.-y. Liu S.-j. Quantitative methodology for the determination of different chemical forms of iron in the Chinese total diet study. Weisheng Yanjiu 1993 22 59. (Inst. Nutr. and Food Hyg. Chinese Acad. Preventive Med. Beijing China). Li P.-j. Ren F.-f. Pan Z.-j. Determination of serum selenium by graphite furnace atomic absorption spec- trometry. Zhonghua Yufang Yixue Zazhi 1993 27 368. (Inst. Prev. Med. Shanghai Med. Univ. Shanghai 200032 China). Desmarais D. Gignac L.D. Bailleux E. M. Comparison of three methods for determining the elemental composition of bryophytes. Acta Bot. Gallica 1994 141 27. (Fac. St.-Jean Univ. Alberta Edmonton Alberta Canada T6G 2E1). Mistry B. S. Reineccius G. A. Jasper B. L. Comparison of gas chromatographic detectors for the analysis of volatile sulfur compounds in foods. ACS Symp. Ser. 1994 564 8. (Dept. Food Sci. Nutr. Univ. Minnesota St. Paul MN 55108 USA). Wyllie S. G. Leach D. N. Wang Y-m. Shewfelt R.L. Sulfur volatiles in Cucumis melo cv. Makdimon (Muskmelon) aroma. Sensory evaluation by gas chrom- atography-olfactometry. ACS Symp. Ser. 1994 564 36. (Sch. Sci. Univ. Western Sydney Richmond 2753 Australia). Celma P. Cabeza L. F. Serrat X. Cot J. Manich A. Tanning process performed in cycles and with hydrogen peroxide in alkaline medium. Ajnidad 1994 51 333.(Inst. Quim. Sarria Barcelona Spain). Gos B. Lewandowski W. Physiocochemical properties of pine dead wood. Ann. Warsaw Agric. Univ. For. Wood Technol. 1994 42 103. (Dept. Phys.-Chem. Background Wood Technol. Warsaw Agric. Univ. Flajnik C. M. Shrader D. Determining lead in blood evaluating deuterium and Zeeman background correc- tion. Am. Clin. Lab. 1994 13 45. (Varian Opt. Spectrosc. Instruments Wood Dale IL 60191 USA). *Warsaw Poland). 9513982 9513983 9513984 9513985 9513986 9513987 9513988 9513989 9513990 9513991 9513992 9513993 9513994 9513995 Rivaro P. Frache R. Mazzucotelli A. Cariati F. Pozzi A. Spectroscopic evaluation of interactions among trace elements and biogenic carbonates in the marine environment.Analyst (London) 1994,119,2485. (1st. Chim. Gen. Univ. Genova Genoa Italy). Vuchkova L. Kosturkova P. Determination of toxic and heavy metals in soils by atomic emission spec- trometry with inductively coupled argon plasma. Anal. Lab. 1993 2 270. (Geol. and Geophys. Co. 1797 Sofia Bulgaria). Chun K.-s. Lee C. Kang HA. Lee J.-d. Classification of Korean ancient coins by neutron activation analysis. Anal. Sci. Technol. 1994,7,293. (Dept. Chem. Hanyang Univ. Seoul 133-791 South Korea). Kojima I. Nomura S. One drop flame atomic absorption spectrometric determination of lead com- bined with solvent extraction after preconcentration with calcium fluoride. Anal. Sci. 1995 11 17. (Dept. Appl. Chem. Nagoya Inst. Technol. Nagoya 466 Japan). Yarbuh A. L.de Anez N. Pena Y. P. de Burguera J. L. Burguera M. Antimony determination in tissues and serum of hamsters infected with Leishmania garnhami and treated with meglumine antimonate. Ann. Trop. Med. Parasitol. 1994 88 37. (Fac. Cien. Univ. Los Andes Merida 5101 Venezuela). Triebskorn R. Koehler H.-R. Flemming J. Braunbeck T. Negele R.-D. Rahmann H. Evaluation of bis( tri-n-butyltin) oxide (TBTO) neurotoxicity in rainbow trout (Oncorhynchus mykiss). I. Behaviour weight increase and tin content. Aquat. Toxicol. 1994 30 189. (Inst. Zool. Univ. Hohenheim Garbenstr. 301 D-70593 Stuttgart Germany). Ito T. Nakano M. Yamamoto Y. Hiramitsu T. Mizuno Y. Hemoglobin-induced lipid peroxidation in the retina a possible mechanism for macular degener- ation. Arch. Biochem. Biophys.1995 316 864. (Dept. Photon Free Radical Res. Japan Immunores. Lab. Co. Ltd. Gunma 370 Japan). Hara K. Yoshizuka M. Fujimoto S. Toxic effects of bis(tributy1tin) oxide on the synthesis and secretion of zymogen granules in the rat exocrine pancreas. Arch. Histol. Cytol. 1994 57 201. (Sch. Med. Univ. Occup. Environ. Health Kitakyushu Japan). Xing D.-j. Guo Q.-x. Ji G.-y. Du K.-q. Sun L.-k. Zhu S.-g. Sun Q.-x. Zhang W.-y. Changes of trace elements Cu Zn Mg Fe in serum and hypothalamus during ET fever in rats. Baiqiuen Yike Daxue Xuebao 1994 20 17. (Dept. Pathophysiol. Norman Bethune Univ. Med. Sci. Changchun China). Li X.-w. Li Q.-m. Liu S.-y. Duan S.-h. Zhang G. Determination of lead copper cadmium and zinc in the internal organs of mice with the differential potentiometric method.Baiqiuen Yike Daxue Xuebao 1994 20 95. (Dept. Chem. Norman Bethune Univ. Med. Sci. Changchun China). Andrews J. C. Nolan J. P. Hammerstedt R. H. Bavister B. D. Role of zinc during hamster sperm capacitation. Biol. Reprod. 1994 51 1238. (Dept. Biochem. Mol. Biol. Pennsylvania State Univ. University Park PA 16802-4504 USA). Yang J. Black J. Competitive binding of chromium cobalt and nickel to serum proteins. Biomaterials 1994 15 262. (Dept. Bioeng. Clemson Univ. Clemson SC Egila J. N. Littlejohn D. Ottaway J. M. Background correction in the determination of chromium in urine and serum matrixes using Zeeman-effect atomic absorp- tion spectrometry. Biokemistri 1993 3 123. (Dept. Chem. Federal Univ. Technol. Yola Nigeria). Koehler H.-R. Koertje K.-H. Alberti G.Content absorption quantities and intracellular storage sites of 29634-0905 USA). Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 351 R9513996 95/3997 95/3998 9513999 9 5/40OO 95/400 1 95/4002 9514003 9 514004 95/4005 9514006 9514007 9514008 352 R heavy metals in Diplopoda (Arthropoda).. BioMetals 1995 8 37. (Inst. Zool. Univ. Hohenheim Stuttgart Germany). Ojo J. O. Oluwole A. F. Durosinmi M. A. Ogunsola 0. J. Akanle 0. A. Spyrou N. M. Baseline levels of elemental concentrations in whole blood plasma and erythrocytes of Nigerian subjects. Biol. Trace Elem. Res. 1994 43 461. (Dept. Phys. Obafemi Awolowo Univ. Ile-Ife Nigeria). Strange R. W. Reinhammar B. Murphy L. M. Hasnain S. S. Structural and spectroscopic studies of the copper site of stellaeyanin.Biochemistry 1995 34 220. (Mol. Biophys. Group Daresbury Lab. Warrington Cheshire UK WA4 4AD). Chatterjee J. De K. Basu S. K. Das A. K. Low- level X-ray exposures on rat skin hyperkeratinization and concomitant changes in biometal concentration. Biol. Trace Elem. Res. 1994 46 203. (Dept. Anat. Burdwan Med. Coll. Burdwan 713 104 India). Fleurence J. Le Coeur C. Influence of digestion procedures on the determination of lead and cadmium levels in the Laminariale Unduria pinnatijida (Wakame) by flame atomic absorption spectrophotometry. Bot. Mar. 1994 37 555. (Centre &Etude et de Valorisation des Algues 22610 Pleubian France). Morgan A. J. Lewis G. Van den Hoven W. E. Akkerboom P. J. Effect of zinc in the form of erythromycin-zinc complex (Zineryt lotion) and zinc acetate on metallothionein expression and distribution in hamster skin. Br.J. Dermatol. 1993 129 563. (Sch. Pure and Appl. Biol. Univ. Wales Coll. Cardiff Cardiff UK CF1 3TL). Falandysz J. Szajek L. Mercury content of mushrooms of Agaricus species from the area of the city of Gdansk. Bromatol. Chem. Toksykol. 1994 27 33. (Univ. Ganskiego Poland). Kozak L. Bubicz M. Mikos-Bielak M. Wards Z. Lead cadmium nickel zinc copper manganese and iron content of fruits available in the region of Lublin. Bromatol. Chem. Toksykol. 1994 27 123. (Akad. Rolniczej Lublin Poland). Falandysz J. Danisiewicz D. Bona H. Metals content of wild growing mushrooms gathered in the Tucholskie and Kaszuby forests. Bromatol. Chem. Toksykol. 1994 27 129. (Wydzialu Chem.Univ. Gdanskiego Gdansk Poland). Falandysz J. Kotecka W. Manganese in food. Part I. Manganese content of food available in northern Poland. Bromutol. Chem. Toksykol. 1994 27 141. ( Wydzialu Chem. Univ. Gdanskiego Gdansk Poland). Suzuki S. Hirata Y. Studies on the determination of strontium in human tooth enamel using nitrous oxide- acetylened emission spectrophotometry. Bull. Kanagawa Dent. Coll. 1994 22 61. (Dept. Dental Health and Public Health Kanagawa Dental Coll. Yokosuka 238 Japan). Johnson S. W. Swiggard P. A. Handel L. M. Brennan J. M. Godwin A. K. Ozols R. F. Hamilton T. C. Relationship between platinum-DNA adduct formation and removal and cisplatin sytotoxicity in cisplatinsensitive and -resistant human ovarian cancer cells. Cancer Res. 1994 54 5911.(Dept. Med. Oncol. Fox Chase Cancer Center Phladelphia PA 19111 USA). Bodnar Z. Mallat T. Baiker A. Reactant induced restructuring and corrosion of germanium-palladium catalysts during hydrogenation reactions. Catal. Lett. 1994 26 61. (Dept. Chem. Eng. Ind. Chem. Swiss Fed. Inst. Technol. CH-8092 Zurich Switzerland). Park G.-s. Lee D.-b. Lee T.-y. Cho Y.-c. Study on the changes of whole blood calcium-magnesium and zinc-copper concentrations during the healing process 9514009 95/40 10 95/4011 95/40 12 9514013 95/4014 95/4015 9514016 95/4017 95/4018 95/4019 95/4020 951402 1 9514022 95/4023 Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 of bone fracture patients. Chungnam Uidae Chapchi 1993 20 143. (Coll. Med. Chungnam Natl. Univ. South Korea). Bartels U.Asche N. Methods for the characterization of fertilizers for forest liming. CLB Chem. Labor Biotech. 1993 44 218. (Landesanst. Oekol. Landschaftsentwickl. Forstplan. Recklinghausen Germany). Omokhodion F. O. Howard J. M. Trace elements in the sweat of acclimatized persons. Clin. Chim. Acta 1994 231 23. (Occup. Health Unit Dept. Preventative and SOC. Med. Univ. Coll. Hosp. Ibadan Nigeria). Zschiesche W. Schaller K. H. Biological indicators for the assessment of human exposure to industrial chemicals. Soluble barium compounds. Comm. Eur. Communities [Rep.] EUR EUR 14815 1994 1,3,5-21. (Luxembourg). de Abreu C. A. de Abreu M. F. van Raij B. Bataglia 0. C. de Andrade J. C. Extraction of boron from soil by microwave heating for ICP-AES determination. Commun. Soil Sci.Plant Anal. 1994 25 3321. (Inst. Agron. Caixa Postal 28 Campinas Brazil). du Toit M. C. du Preeez C. C. Indirect atomic absorption determination of total and inorganic sulfur in low organic matter soils. Commun. Soil Sci. Plant Anal. 1995 26 69. (Inst. Soil Climate and Water Pretoria 0001 South Africa). Ferreira A. M. R. Rangel A. 0. S. S. Lima J. L. F. C. Flow injection systems with a stream splitting and a dialysis unit for the soil analysis of sodium and potassium by flame emission spectrometry and calcium and magnesium by atomic absorption spectrophotome- try. Commun. Soil Sci. Plant Anal. 1995,26,183. (Escola Sup. de Biotecnol. Univ. Catolica Portuguesa Oporto 4200 Portugal). Veljanov S. Specific method for the determination of zinc in wine by flame atomic absorption spectroscopy Conf.Adv. Biochem. Eng. Three-Day Symp. 2nd. Inst. Chem. Eng. 1994. 148. Tandon V. Roy B. Analysis of trace elements of some edible trematodes parasitizing the bovine hosts. Curr. Sci. 1994 67 548. (Dept. Zool. North-Eastern Hill Univ. Shillong 793 014 India). Lori J. A. Bonire J. J. Jalil N. S. N. Difference in concentration of some mineral elements in the tissue and bark of white yam (Dioscorea rotundata). Discovery Innovation 1994,6 14. (Natl. Res. Inst. Chem. Technol. Zaria Nigeria). Wang E.-x. Trace mercury determination in Zn/MnO battery. Dianchi 1994 24 291. (Inst. Chem. Power Sources Minist. Light Ind. Jiangsu 215006 China). Green N. R. Ferrando A. A. Plasma boron and the effects of boron supplementation in males. Environ.Health Perspect. Suppl. 1994 102 73. (Dept. Nutr. and Food Sci. Auburn Univ. Auburn AL USA). Moseman R. F. Chemical disposition of boron in animals and humans. Environ. Health Perspect. Suppl. 1994 102 113. (Radian Corp. Res. Triangle Park NC USA). Romeu-Moreno A. Aguilar C. Arola L. Mas A. Respiratory toxicity of copper. Environ. Health Perspect. Suppl. 1994,102,339. (Dept. Biochem. and Biotechnol. Univ. Rovira i Virgili Tarragona 43005 Spain). Suszcynsky E. M. Shann J. R. Phytotoxicity and accumulation of mercury in tobacco subjected to different exposure routes. Environ. Toxicol. Chem. 1995 14 61. (Dept. Biol. Sci. Univ. Cincinnati Cincinnati Lombeck I. Fuchs A. Zinc and copper in infants fed breast-milk or different formula. Eur. J. Pediatr.. 1994 153 770. (Univ.Kinderkrankenhaus D-40225 Dusseldorf Germany). OH 45221-0006 USA).9514024 9514025 95/4026 9514027 9514028 9514029 9514030 9 51403 1 9514032 9514033 9 5/40 34 951403 5 9 51403 6 9514037 Sestakova I. Miholova D. Slamova A. Mader P. Szakova J. Determination of Cd Cu and Pb in animal tissues-comparison of electrochemical results obtained with a new polarographic system and atomic spec- troscopy. Electroanalysis ( N . X I 1994 6 1057. (J. Heyrovsky Inst. Phys. Chem. Acad. Sci. Czech Republic Prague 8 182 23 Czech Republic). Tahvonen R. Kumpulainen J. Lead and cadmium contents in Finnish breads. Food Addit. Contam. 1994 11 621. (Agric. Res. Centre of Finland Central Lab. SF-31600 Jokioinen Finland). Coni E. Bocca A. Ianni D. Caroli S. Preliminary evaluation of the factors influencing the trace element content of milk and dairy products.Food Chem. 1994 52 123. (1st. Super. Sanita Viale Regina Elena 00161 Rome Italy). Lange-Hesse K. Investigations of properties and bind- ing forms of cadmium and nickel in protein extracts by ultra-/diafiltration photometry and atomic absorption spectrometry. Fresenius’ J. Anal. Chem. 1994 350 68. (Bodenseewerk Perkin-Elmer GmbH D-40549 Dusseldorf Germany). Yaman M. Guecer S. Determination of vanadium in biological matrixes by flame atomic absorption spec- trometry with activated carbon enrichment. Fresenius’ J. Anal. Chem. 1994 350 504. (Dept. Chem. Univ. Firat Elazig TR-23 119 Turkey). Jian S.-q. Dong M.-x. Xie F.-m. Analysis of agricul- tural samples. Fenxi Shiyanshi 1994,13( 6) 93. (Chinese Acad.Agric. Sci. Beijing 100081 China). Lamb D. J. Leake D. S. Iron released from transferrin at acidic pH can catalyze the oxidation of low density lipoprotein. FEBS Lett. 1994 352 15. (Dept. Biochem. and Physiol. Sch. Animal and Microbial Sci. Univ. Reading Whiteknights PO Box 228 Reading Berks. UK RG6 2AJ). Kochi S. K. Schiavo G. Mock M. Montecucco C. Zinc content of the Bacillus anthracis lethal factor. FEMS Microbiol. Lett. 1994 124 343. (Lab. Genet. Mol. Toxines (URA 557 CNRS) Inst. Pasteur Paris France). Yao J.-y. Hu Q.-l. Xie W.-b. Determination of chromium(II1) and chromium(v1) in fish bone meal by flame atomic absorption spectrometry after coprecipi- tation with ferric hydroxide. Guangpuxue Yu Guangpu Fenxi 1994 14(5) 69. (Changchun Inst. Appl.Chem. Acad. Sin. Changchun 130022 China). Xu L.q. Liu Y.-h. Zhou A.-m. Determination of cadmium in biological samples by ICP-AES with online chelating resin column preconcentration. Guangpuxue Yu Guangpu Fenxi 1994 14(6) 65. (Shanghai Inst. Metall. Acad. Sin. Shanghai 200050 China). Xu D.q. Study on the effects of matrix modifiers on the determination of germanium in serum by graphite furnace atomic absorption spectrometry. Guangpuxue Yu Guangpu Fenxi 1994 14(6) 77. (Dept. Public Health Hebei Med. Coll. Shijiazhuang 05001 7 China). Mo S.-j. Determination of manganese in blood and urine samples by graphite furnace atomic absorption spectroscopy. Guangpuxue Yu Guangpu Fenxi 1994 14(6) 95. (Dept. Chem. South China Normal Univ. Canton 510631 China). Zhu Z.-g. Gu M.Guo B.-j. Lu H.-z. Determination of the serum copper content in 142 healthy adults. Guangpuxue Yu Guangpu Fenxi 1994 14(6) 111. (Air- Force Med. Coll. Jilin 132011 China). Cai S.-a Xu L. Yang Y.-q. Hu C.-y. Jurs P. C. Ball J. W. Dixon S. L. Classification of human senile cataract lenses based on metal contents using neural networks. Gaodeng Xuexiao Huaxue Xuebao 1994 15 982. (First Clin. Coll. Norman Bethune Univ. Me& Sci. China). 9514038 9 514039 9514040 9514041 9514042 9514043 9514044 9514045 9514046 9514047 9514048 9514049 9514050 9514051 9514052 9 51405 3 Frosch D. Ruthenberg K. Early Thuringian glass containing arsenic. Glass Sci. Technol. (Frankfurt1 Main) 1994 67 N98. (Chem. Lab. Fachhochsch. Coburg Coburg Germany). Koelling S. Kunze J. Analysis of the chemical composition of ancient glasses.GIT Fachz. Lab. 1994 38 1119. (Zentrallab. Chem. Anal. Tech. Univ. Hamburg-Harburg D-2107 1 Hamburg Germany). Kong L. Huo R. Pei M. Study of the inhibition kinetics and mechanism of banana peel polyphenoloxid- ase-catalyzed reaction. Huanan Ligong Dame Xuebao Ziran Kexueban 1994 22 81. (Dept. Appl. Chem. South China Univ. Tech. Guangzhou China). Li B.-m. Study and preparation of environmental soil standard reference materials. Huanjing Kexue 1994 15 19. (Environ. Monitoring Centre Heilongjiang Prov. China). Wastiaux A. Blanchard O. Honnons S. Possible application of urinary analysis to estimate dissolution of some man-made vitreous fibres. Enuiron. Health Perspect. Suppl. 1994 102 217. (Inst. Natl. Environ. Ind. et Risques (INERIS) 60550 Verneuil-en-Halatte France).Li B.q. Li M.-h. Wang Z.-b. Determination of trace barium in common salt by graphite furnace. Haihuyan Yu Huagong 1994 23 13. (Inst. Salt Prod. Ind. Minist. Light Ind. China). Zhang L.-q. Wang Y.-a. Gao X.-r. Purification of Cu-Zn superoxide dismutase. Hebei Shifan Dame Xuebao Ziran Kexueban 1994 18 79. (Hebei Normal Univ. Shijiazhuang 050016 China). Moreno-Rojas R. Zurera-Cosano G. Amaro-Lopez M. A. Concentration and seasonal variation of calcium magnesium sodium and potassium in raw cow ewe and goat milk. Int. J. Food Sci. Nutr. 1994 45 99. (Dept. Food Hyg. and Technol. Univ. Cordoba Cordoba 14005 Spain). Bolletti P. Menci L. Tellini L. Lead copper and zinc in wines produced in Arezzo. Ind. Beuande 1994 23 327. (Serv.Multizonale Prev. della USL 23 di Arezzo 52100 Arezzo Italy). Schroeder W. P. Arellano J. B. Bittner T. Baron M. Eckert H.-J. Renger G. Flash-induced absorption spectroscopy studies of copper interaction with photo- system 11 in higher plants. J. Biol. Chem. 1994 269 32865. (Dept. Biochem. Stockholm Univ. $106 91 Stockholm Sweden). Surovell T. Atomic spectra-graph. J. Chem. Educ. Software Ser. C 1994 6C 23. (Project SERAPHIM Univ. Wisconsin Madison WI 53706-1396 USA). Peters R. J. B. de Leer E. W. B. Versteegh J. F. M. Identification of halogenated compounds produced by chlorination of humic acid in the presence of bromide. J. Chromatogr. 1994 686 253. (Dept. Anal. Chem. TNO Inst. Environ. Sci. Schoemakerstr. 97 2600 JA Delft Netherlands). Holm P. E. Christensen T.H. Tjell J. C. McGrath S. P. Heavy metals in the environment. Speciation of cadmium and zinc with application to soil solutions. J. Environ. Qual. 1995 24 183. (Inst. Environ. Sci. Eng. Tech. Univ. Denmark Lyngby DK 2800 Denmark). Bunton T. E. Frazier J. M. Extrahepatic tissue copper concentrations in white perch with hepatic copper storage. J. Fish Biol. 1994 45 627. (Sch. Med. Johns Hopkins Univ. Baltimore MD 21205 USA). Tahvonen R. Kumpulainen J. Levels of selected elements in Finnish breads. J. Food Compos. Anal. 1994 7 83. (Central Lab. Agric. Res. Center Finland SF-3 1600 Jokioinen Finland). Cary E. E. Grunes D. L. Dallyn S. L. Pearson G. A. Peck N. H. Hulme R. S. Plant Fe A1 and Cr Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 353R9514054 9514055 9 51405 6 9514057 9514058 9514059 9514060 9514061 9514062 9514063 9514064 9514065 9514066 9514067 354 R concentrations in vegetables as influenced by soil inclusion.J. Food Qual. 1994 17 467. (US Plant Soil and Nutr. Lab. ARS Ithaca NY 14853 USA). Hutter G. Moshman D. Comparisons among lead paint field screening test methods. J. Hazard. Muter. 1994 40 1. (Triodyne Environ. Eng. Inc. Niles IL 60714 USA). Linkerhaegner M. Stan H.-J. Rimkus G. Detection of nitro musks in human fat by capillary gas chromatog- raphy with atomic emission detection (AED) using programmed temperature vaporization (PTV). J. High Resolut. Chromatogr. 1994 17 821. (Inst. Food Chem. Tech. Univ. Berlin D-13355 Neumuenster Germany). Cha K.-w. Park S.-h. Choi J.-s. Determination of selenium in foods by HG-AAS.J. Korean Chem. SOC. 1994 38 891. (Dept. Chem. Inha Univ. Inchon 401-751 South Korea). Chattaraj S. Das A. K. Indirect AAS determination of anionic surfactants by formation of an ion-pair with bis-(2-benzoylpyridine thiosemicarbazone)cobalt(m). Indian J. Chem. Technol 1994 1 98. (Dept. Chem. Univ. Burdwan Burdwan 713 104 India). Lux O. Naidoo D. Assessment of biological variation components of copper zinc and selenium. J. Nutr. Biochem. 1995 6 43. (Dept. Clin. Chem. Prince of WalesIPrince Henry Hosp. Randwick Australia). Hawkins N. M. Coffey S. Lawson M. S. Delves H. T. Potential aluminium toxicity in infants fed special infant formula. J. Pediatr. Gastroenterol. Nutr. 1994 19 377. (Med. Unit Inst. Child Health London UK WClN 1EH).Wilkinson R. E. Duncan R. R. Berry C. Element absorption by sorghum root tips as influenced by multiple ion-channel and ion-pump inhibitors. J. Plant Nutr. 1994 17 2235. (Dept. Crop Soil Sci. Georgia St. Griffin GA 30223-1797 USA). Anger F. S. Anger J.-P. H. Sado P. A. Chevanne F. Germanium absolute and relative bioavailability in rabbit. J. Pharm. Belg. 1994 49 395. (Fac. Sci. Pharm. et Biol. Lab. Pharm. Glenique Biopharm. and Pharm. Clin. 35043 Rennes France). Wilkinson R. E. Duncan R. R. Berry C. Plant mineral contents of root tips from four sorghum cultivars after exposure to the anion channel blocker SITS. J. Plant Nutr. 1994 17 2189. (Dept. Crop Soil Sci. Georgia St. Griffin GA 30223-1797 USA). Day M. P. Zhang B. Martin G. J. Determination of the geographical origin of wine using joint analysis of elemental and isotopic composition.11-Differentiation of the principal production zones in France for the 1990 vintage. J. Sci. Food Agric. 1995 67 113. (Lab. NMR and Chem. Reactivity Univ. Nantes F-44072 Nantes France). Watanabe S. Kanetaka S. Miyata K. Nakamura Y. Consideration on the distribution of metal elements in human hair. J. SCCJ 1994 28 262. (NICCA Chem. Co. Ltd. Hukui 910 Japan). Jun S. Lima J. L. F. C. Montenegro M. C. B. S. M. Sequential flow-injection determination of ionic and total calcium in saliva. J. Trace EFem. Electrolytes Health Dis. 1994 8 93. (Dept. Quim. Fis. Fac Farm. Oporto 4000 Portugal). Zheng W. Winter S. M. Kattnig M. J. Carter D. E. Sipes I. G. Tissue distribution and elimination of indium in male Fischer 344 rats following oral and intratracheal administration of indium phosphide.J. Toxicol. Environ. Health 1994 43 483. (Dept. Pharmacol. Toxicol. Coll. Pharm. Univ. Arizona Tucson AZ USA). Van Cauwenbergh R. Robberecht H. Deelstra H. Picramenos D. Kostakopoulos A. Selenium concen- tration in serum of healthy Greek adults. J. Trace Elem. 9514068 9514069 9514070 951407 1 9514072 9 51407 3 9514074 9514075 9514076 9514077 9514078 9514079 9514080 9514081 9514082 Electrolytes Health Dis. 1994 8 99. (Dept. Pharm. Sci. Univ. Antwerp B-2610 Wilrijk Belgium). Kim. S.-k. Park S.-j. Choi D.-d. Purification and characterization of superoxide dismutase from Mytilus edulis. Korean Biochem. J. 1994,27,427. (Dept. Chem. Natl. Fisheries Univ. Pusan Pusan 608-737 South Korea).Kaiser C. Muller H. A. G. Schmitt Y. Geisen H. P. Schott F. J. Should reference values for calcium be revised? Klin. Labor 1994 40 599. (Inst. Laboratoriumsmed. Klin. Am Eichert D-73035 Goppingen Germany). Pohl B. Lange M. Determination of tin in urine and bismuth in blood serum with graphite furnace AAS. Laboratoriumsmedizin 1994 18 38. (Varian GmbH D-64289 Darmstadt Germany). Nott J. A. Nicolaidou A. Variable transfer of detoxified metals from snails to hermit crabs in marine food chains. Mar. Biol. (Berlin) 1994 120 369. (Plymouth Mar. Lab. Plymouth Devon UK PL1 2PB). Weichen A. Tait D. Stable strontium in milk and milk powder in the Federal Republic Germany. Milchwissenschaft 1994 49 603. (Inst. Chem. Phys. Bundesanstalt Milchforschung D-24103 Kiel Germany).Callahan H. L. Roberts W. L. Rainey P. M. Beverley S. M. PGPA gene of Leishmania major mediates antimony (Sbm) resistance by decreasing influx and not by increasing efflux. Mol. Biochem. Parasitol. 1994 68 145. (Dept. Biol. Chem. and Mol. Pharm. Harvard Med. Sch. Boston MA 02115 IJSA). Wu Y.4 Wang G.4 Zhang Z.-y. Zhang Q. Determination of copper zinc and tin in canned foods by atomic absorption spectrometry. Nanjing Huagong Xueyuan Xuebao 1994 16 40. (Dept. Appl. Chem. Nanjing Inst. Chem. Technol. Nanjing 210009 China). Tamura K. Azuma J. Determination of carbon in soil humus by inductively coupled plasma emission spec- trometry. Nippon Dojo Hiryogaku Zasshi 1994 65 560. (Fac. Agric. Kobe Univ. Kobe 657 Japan). Hara K. Yoshizika M. Doi Y. Fujimoto S.Effect of bis(tributy1 tin) oxide on permeability of the blood- brain barrier a transient increase. Occup. Environ. Med. 1994 51 735. (Dept. Anat. Univ. Occup. Environ. Health Kitakyushu 807 Japan). Droz V. Dubois H. Jeanneret G. Nydegger S. Gold dosage. AAS determination of the reproducibility of metal dosage. Gold in electrodeless baths. OberJEaechen Werkst. 1994 35 29. (Lab. Dubois S.A. CH-1305 La Chaux-de-Fonds Switzerland). Gorecka H. Gorecki H. Dobrzanski Z. Use of ICP method in determination of cadmium and other trace elements in fertilizers and soils. Pr. Nauk. Inst. Technol. Nieorg. Nawozow Miner. Politech. Wroclaw 1994 40 100. (Inst. Technol. Nieorg. Nawozow Miner. Politech. Wroclawska 50-370 Wroclaw Poland). Maxon M. E. Tjian R. Transcriptional activity of transcription factor IIE is dependent on zinc binding.Proc. Natl. Acad. Sci. U. S . A. 1994. 91. 9529. (Howard Hughes Med. Inst. Univ. California; Berkeley CA 94720 USA). Jaser M. A. El-Yazigi A. Croft S. L. Pharmacokinetics of antimony in patients treated with sodium stibogluconate for cutaneous leishmaniasis. Pharm. Res. 1995 12 113. (Dept. Med. Parasitol. Univ. London London UK). Zhao F. McGrath S. P. Extractable sulfate and organic sulfur in soils and their availability to plants. Plant Soil 1994 164 243. (Soil Sci. Dept. AFRC Inst. Arable Crops Res. Harpenden Herts UK AL5 254). Ganji V. Kies C. V. Zinc bioavailability and tea consumption. Studies in healthy humans consuming Journal of Analytical Atomic Spectrometry November 1995 Vol. 109514083 9514084 9514085 9 5/40 8 6 9 5/40 8 7 9 514088 9 51408 9 9514090 9514091 9514092 9514093 9514094 9514095 9514096 self-selected and laboratory-controlled diets.Plant Foods Hum. Nutr. (Dordrecht Neth.;) 1994 46 267. (Dept. Health Sci. California State Univ. San Bernardino CA 92407 USA). Ballesteros E. Gallego M. Valcarcel M. Maier E. Determination of calcium magnesium and potassium in beech leaves by flow-injection analysis and atomic- absorption spectrometry. Quim. Anal. (Barcelona) 1992 11 147. (Fac. Cienc. Univ. Cordoba Cordoba 14004 Spain). Jimenez de Blas O. Pereda de Paz J. L. Hernandez Mendez J. FIA system with injection prior to liquid- liquid extraction applied to the indirect determination of dithiocarbamate fungicides by atomic absorption spectroscopy.Quim. Anal. (Barcelona) 1992 11 173. (Dept. Anal. Chem. Univ. Salamanca Salamanca 37008 Spain). Moreno R. R. Amaro Lopez M. Canal Ruiz C. Garcia Gimeno R. Zurera Cosano G. Mineral content in Spanish sterilized milk. Rev. Esp. Cienc. Tecnol. Aliment. 1994 34 323. (Dept. Bromatol. Tecnol. 10s Alimentos Univ. Cordoba Cordoba 14005 Spain). Baldini M. Molinaro M. G. Stacchini P. Zanasi F. Corni R. Leoni V. Average weekly intake of mercury in the diet in Italy. Riv. Sci. Aliment. 1994 23 177. (Lab. Alimenti 1st. Superiore Sanita Roma Italy). Huang S.-p. Du R. Chen L. Determination of trace elements in various alcoholic drinks of Shanxi pro- duction. Shanxi Daxue Xuebao Ziran Kexueban 1994 17 315. (Test Anal. Centre Shanxi Univ. China). Wang W.-x. Ding S.-z. Xu H.-w.Effects of exercise on the rat heart mitochondria1 membrane function. Shengwu Huaxue Yu Shengwu Wuli Xuebao 1994 26 243. (Dept. Phys. Educ. East China Normal Univ. Shanghai 200062 China). Wei Y.-z. Song Q.-h. Liu L. Determination of germanium in foods by graphite furnace-atomic absorp- tion spectrophotometry. Shipin Yu Fajiao Gongye 1994 3 30. (Sci. Res. Inst. Food Fermentation Ind. Minist. Light Ind. Beijing China). Maitani T. Xing D.-r. Terai R. Yoshihira K. Application of vacuum-ultraviolet ICP atomic emission spectrometry for tests of carrageenan. Shokuhin Eiseigaku Zasshi 1994 35 631. (Natl. Inst. Health Sci. Tokyo 158 Japan). Yasui A. Suzuki T. Shindoh K. Effects of major elements on emission in inductively coupled plasma atomic emission spectroscopy for determination of inorganic elements in food.Shokuhin Sogo Kenkyusho Kenkyu Hokoku 1994 58 37. (Natl. Food Res. Inst. Tsukuba 305 Japan). Arnaud J. Favier A. Copper iron manganese and zinc contents in human colostrum and transitory milk of French women. Sci. Total Environ. 1995 159 9. (Lab. Biochim. C CHUG BP 217 38043 Grenoble 9 France). Saatci A. O. Gezer S. Berk T. Gener G. Ergin M. Copper in tears. Turk. J. Med. Sci. 1994 21 107. (Fac. Med. Dokuz Eylul Univ. Izmir Turkey). Offenbacher E. G. Promotion of chromium absorption by ascorbic acid. Trace Elem. Electrolytes 1994 11 178. (Health Sci. Res. Inst. St. Luke’s-Roosevelt Hosp. Center New York NY 10025 USA). Brushwood D. E. Perkins H. H. Jr. Determining the metal content of cotton. Text. Chem. Color. 1994 26 32.(Cotton Qual. Res. Stn. U.S. Dept. Agric. Res. Serv. Clemson SC USA). Evans D. J. Analysis of crosslinked silicones on wool by atomic absorption spectroscopy. Text. Res. J. 1995 65 118. (Geelong Lab. CSIRO Div. Wool Technol. Belmont 3216 Australia). 9514097 9514098 9514099 9514 100 9514101 9514102 9 514 103 9 514 104 9514105 9 514 106 9514107 9 514 1 08 9514109 95/41 10 Liu L.-x. Zhang W. Sui G.-y. Zeng X.-l. Qiu C.-x. Liu H. Analysis of manganese zinc copper iron and magnesium contents in 91 kinds of main food from Jining. Weisheng Yanjiu 1994 23 306. (Dept. Prevention Jining Med. Coll. Jining 2721 13 China). Zou D.4 Gao S.-y. Studies on trace metal concen- trations in marine organisms from Meizhou Bay. Xiamen Daxue Xuebao Ziran Kexueban 1994,33 386. (Dept.Oceanogr. Inst. Subtropical Oceanogr. Xiamen China). Wang Q.-y. Wu N.-c. Copper and zinc content in serum erythrocytes and leukocytes in normal adults. Zhongguo Yike Daxue Xuebao 1994 23 233. (Inst. Respiratory Dis. China). Yu X.4 Lu J.-r. Pan C.-m. Preparation for determi- nation of trace elements in tissues by atomic absorption spectrophotometry. Zhejiang Yike Daxue Xuebao 1994 23 189. (Affiliated Children Hosp. Zhejiang Med. Univ. Hangzhou China). He B.-p. Zhao D.-s. Zhao L. Wang Y. Wang G.-q. Bao S.-f. Li D.-f. Deng X.-x. Deng J.-f. Seven elements in patients with heart disease and their relationship with blood pressure and biochemical indexes. Zhonghua Yixue Zazhi 1994 74 492. (Dept. Chem. Second Military Med. Univ. Shanghai 200433 China). Ikebe Y. Tamura H.Sumya H. Adjustment technique for primary ion beams. Jpn. Kokai Tokkyo Koho JP 06,215,728 [94,215,728] (Cl. H01 J49/14) 05 Aug 1994 Appl. 9315,618 18 Jan 1993; 4 pp. (Hitachi Ltd. Japan). Saito H. Asako K. Tsuda N. Takenaka T. Manufacture of semiconductor wafers and SIMS (sec- ondary ion mass spectroscopy) analysis. Jpn. Kokai Tokkyo Koho JP 07 58,304 [95 58,3041 (Cl. HOlL27/12) 03 Mar 1995 Appl. 931217,985 10 Aug 1993; 9 pp. (Shinetsu Handotai Kk Japan). Shichi H. Mitsui Y. Kanebori K. Ninomya T. Okudaira H. Irie T. Takaguchi M. Matsura Y. Ooyu S. Myao M. Ion generation method and apparatus for surface elemental analysis. Jpn. Kokai Tokkyo Koho JP 07 65,776 [95 65,7761 (Cl. HOlJ37/252) 10 Mar 1995 Appl. 931207,935 23 Aug 1993; 11 pp. (Hitachi Ltd. Japan). Murphy D.M. Thomson D. S. Laser ionization mass spectroscopy of single aerosol particles. Aerosol Sci. Technol. 1995 22 237. (Aeronomy Lab. NOAAIERL Boulder CO 80303 USA). Jenett H. Luczak M. Dessenne 0. Plasma secondary- neutral and secondary-ion mass spectrometry investi- gations on ceramicfcopper powder pellets. Anal. Chim. Acta 1994 297 285. (Inst. Spektrochem. Angew. Spektrosk. Bunsen-Kirchhoff-Str. 11 Postfach 101352 D-44013 Dortmund Germany). Lantzsch J. Bushaw B. A Herrmann G. Kluge H.-J. Monz L. Niess S. Otten E. W. Schwalbach R. Schwarz M. et al. Trace analysis of the radio- nuclides 90Sr and 89Sr in environmental samples. I Laser mass spectrometry. Angew. Chem. Int. Ed. Engl. 1995 34 181. (Inst. Phys. Univ. D-55099 Mainz Germany). Rajasekar P. Chakraborty P.SIMS in the perspectives of some high-T superconducting materials. Ann. Univ. Mariae Curie-Sklodowska Sect. AAA 1994 46 375. (Saha Inst. Nucl. Phys. Calcutta India). Ling Y.-c. Wang J.-p. Yeh M.-h. Liu K.-s. Lin I.-n. Secondary ion mass spectrometric studies of SrTiO buffering effect on (Pb,- Lax)(Zr,- .Tiy)1-x,4 O3 thin films prepared by pulsed laser deposition. Appl. Phys. Lett. 1995 66 156. (Dept. Chem. Natl. Tsing Hua Univ. Hsinchu 30043 Taiwan). Madronero A. Verdu M. Hydrogen content evaluation in vapour-grown carbon fibres by SIMS. Carbon 1995 Journal of Analytical Atomic Spectrometry November 1995 V01.10 355R9514 1 1 1 9514112 95/41 13 95/41 14 9514115 9514 1 1 6 9514117 974 1 1 8 95/41 19 9514120 9514 12 1 9 514 1 22 9514 123 9514 124 356 R 33 247.(Centro Nacl. Invest. Metal. Madrid 28040 Spain). Zhao J. Wang Y.-c. Photoluminescence study on InGaAsIInP MQW structure with IT' Ne+-implant induced compositional disordering. Chin. Phys. Lett. 1994 11 713. (Dept. Phys. Tianjin Normal Univ. Tianjin 300074 China). Martin R. R. MacPhee J. A. Kyotani T. Tomita A. Secondary ion mass spectroscopy (SIMS) imaging as a tool for studying catalytic activity in coal conversion Conf. Proc. - Int. Conf. Coal Sci. 7th. Can. Natl. Organ. Comm. 7th Int. Conf. Coal Sci. Devon Canada 1993. 535. Czerwinski F. Sproule G. I. Graham M. J. Smeltzer W. W. "0-SIMS study of oxide growth on nickel modified with Ce implants and CeO coatings. Corros. Sci. 1995 37 541. (Inst. Mater. Res. McMaster Univ. Hamilton Ontario Canada L8S 4M1).Auleytner J. Adamczewska J. Barcz A. Gorecka J. Reginski K. X-ray electrono-optical and SIMS charac- terization of Si crystals implanted with Bi ions before and after rapid thermal annealing. Cr.yst. Res. Technol. 1995 30 129. (Inst. Phys. Polish Acad. Sci. Warsaw Poland). Gill C. G. Development of a laser ablation quadrupole ion trap mass spectrometer for direct spectrometry of solid samples. Diss. Abstr. Int. B 1995 55 3327. (Univ. British Columbia Vancouver British Columbia Canada). Jedlinski J. Bernasik A. Borchardt G. Mitchell D. F. Sproule I. G. Graham M. J. Application of SIMS method for studying corrosion mechanisms at high temperatures. Elektronika 1994,35,50. (Akad. Goniczo- Hutnicza Krakow Poland). Lin FA. Huang R.-b. Liu Z.-y. Huang F. Zheng L.-s. Laser plasma mass spectrometric analysis of solid inorganic samples.Fenxi Ceshi Xuebao 1994 13 60. (Dept. Chem. Xiamen Univ. Xiamen 361005 China). Zhao S.-k. Zhong F. Zha Q.-m. Chen D. Research- grade laser microprobe time-of-flight mass spectrometer and its applications. Fenxi Huaxue 1994 22 1079. (Instrum. Anal. and Res. Centre Zhongshan Univ. Canton 510275 China). Koch K. H. Sommer D. Grunenberg D. Analysis of oxide dusts by SNMS. Fresenius' J. Anal. Chem. 1995 351 125. (Chem. Anal./Tech. Krupp lloesch Stahl AG D-44120 Dortmund Germany). Zhu Y.-k. Wang M.-x. Zhang N.-m. Yan G.-h. Hong W.-y. Application of SIMS in HL-1 tokamak experiment. Hejubian Yu Dengliziti Wuli 1994 14 47. (Southwestern Inst. Phys. Chengdu 610041 China). Tourmann J.-L. Kaufmann R. Laser microprobe mass spectrometric (LAMMS) study of quartz-related and non-quartz-related factors of the specific harmfulness of coal mine dusts.Inhaled Part. VII Proc. Int. Symp. 7th 1991. Pergamon Oxford UK 1994. 455. Hou X.-q. Ren D. Mao HA. Lei J.-j. Jin K.-l. Chu P. K. Reich F. Wayne D. H. Application of imaging TOF-SIMS to the study of some coal macerals. Int. J. Coal Geol. 1995 27 23. (Beijing Grad. Sch. China Univ. Min. and Technol. Beijing 100083 China). Rajasekar P. Ray N. Dey S. D. Bandyopadhyay S. K. Barat P. Sen P. Chakraborty P. Caccavale F. BertonceUo R. Studies of binding energies of various components in bismuth-based cuprate superconductors through secondary ion mass spectrometry and X-ray photoelectron spectroscopy. J. Appl. Phys. 1995 77 343. (Saha Inst.Nucl. Phys. Calcutta 700064 India). Kokai F. Taniwaki M. Koga Y. Kakudate Y. Fujiwara S. Fukada K. Kawaguchi M. Laser ioniz- ation time-of-flight mass spectrometric study on laser ablation of a graphite-like material of (BC,N) composi- Journal of Analytical Atomic Spectrometry Novembei 9514125 95/41 26 9514127 9514 128 9514129 9.514130 9514 1 3 1 9514132 9514133 95/4134 9514135 95/4136 9514137 9514138 1995 Vol. 10 tion. J. Appl. Phys. 1995 77 2220. (Laser Lab. Inst. Res. and Innovation Chiba 277 Japan). Aschauer E. Fasching R. Urban G. Nicolussi G. Husinsky W. Surface characterization of thin-film platinum electrodes for biosensors by means of cyclic voltammetry and laser SNMS. J. Electroanal. Chem. 1995 381 143. (Inst. Allg. Elektrotech. und Elektronik Tech.Univ. Wien Gusshausstr. 27-29 A-1040 Wien Austria). Zou H. Hood G. M. Nakajima H. Roy J. A. Schultz R. J. Solid solubility of Ni and Co in a-Zr secondary ion mass spectrometry study. J. Nucl. Mater. 1995 223 186. (Res. Chalk River Labs. At. Energy Canada Ltd. Chalk River Ontario Canada). Savard M. M. Veizer J. Hinton R. Cathodolumines- cence at low Fe and Mn concentrations SIMS study of zones in natural calcites. J. Sediment. Res. Sect. A. 1995 65 208. (Geol. Surv. Canada Quebec Geosci. Centre Ste-Foy Quebec Canada G1V 4C7). Bernasik A. Nowotny J. Scherrer S. Weber S. SIMS measurements of segration depth profiles in Cr-doped COO. Metall. Foundry Eng. 1994 20 105. (Fac. Metall. and Mater. Eng. Univ. Min. and Metall. 30-059 Krakow Poland). Jedlinski J. Borchardt G.Bernasik A. Scherrer S. Ambos R. Rajchel B. Redistribution of major and minor alloy components in scales formed during early stages of oxidation on FeCrAl alloys studied by means of SIMS and SNMS Microsc. Oxid. 2 Proc. Int. Conf 2nd. Inst. Mater. London UK 1993. 445. Prescott R. Mitchell D. F. Graham M. J. SIMS study of the effect of Y and Zr on the growth of oxide on P-NiA1 Microsc. Oxid. 2 Proc. Int. Conf. 2nd. Inst. Mater. London UK 1993. 455. Odom R. W. di Brozolo F. R. Laser ionization mass spectrometry [in micro-analysis of solids] Microanal. Solids. Plenum New York NY USA 1994. 269. Eiden G. C. Anderson J. E. Nogar M. S. Resonant laser ablation semiquantitative aspects and threshold effects. Microchem. J. 1994,50,289. (Chem. Sci. Technol. Div. Los Alamos Natl.Lab. Los Alamos NM 87545 USA). Smirnov V. K. Simakin S. G. Makarov V. V. Potapov E. V. In-depth analysis of ultrathin doped layers of Ge in silicon by secondary-ion mass spec- trometry. Mikroelektronika 1994 23 61. (Inst. Mikroelecktron. Yaroslavl Russia). Burns M. S. Taffet R. Hitzman C. J. Inward permeability of lithium and rubidium following light exposure to the rat retina measured by SIMS. Microbeam Anal. (Deerfield Beach Flu.) 1995 4 47. (Sch. Med. Univ. California Davis Sacramento CA 95816 USA). Takai K. Seki J.4 Yamauchi G. Homma Y. Observation of trapping sites for hydrogen an deuterium in high-strength steels by using secondary ion mass spectrometry. Nippon Kinzoku Gakkaishi 1994 58 1380. (NTT Tech. Assistance Support Center Tokyo Japan). Wu X.-s.Lin Z.-j. Ji C.-z. Yang X.-z. Ion beam and SIMS analysis on damage of GaAs doped with N'. Nucl. Sci. Tech. 1994 5 154. (Dept. Phys. Beijing Normal Univ. Beijing 100875 China). Homolka P. Husinsky W. Nicolussi G. Betz G. Li X. Matrix effects of secondary neutrals Laser postioniz- ation investigations of particles sputtered from clean and oxidized metals. Phys. Rev. B Condens. Matter 1995 51 4665. (Inst. Allemeine Phys. Tech. Univ. Wien A-1040 Wien Austria). Nicolussi G. Husinsky W. Gruber D. Betz G. Formation of metastable excited Ti and Ni atoms during ion sputtering. Phys. Rev. B Condens. Matter,9514139 9514140 9514141 9514 142 9514143 9514144 95/4145 9514146 9514 147 9514 148 9 514 149 95/4150 9514151 9514152 9514153 1995 51 8779. (Inst. Allg. Phys. Tech. Univ.Wien A-1040 Wien Austria). Nebauer E. Merkel U. Weissbrodt P. Wuerfl J. Annealing behaviour of Au/LaB,/Au/Ni/Ge systems on n-GaAs studied by the SNMS technique. Phys. Status Solidi A 1994 146 697. (Ferdinand-Braun-Inst. Hoechstfrequenztech. D- 12489 Berlin Germany). Sparrow G. R. Foley J. Quantitative evaluation and control of surface chemistry affecting electronic devices. ISS and SIMS surface analysis. Proc.-Electrochem. SOC. 1994 94 303. (Cortec Corp. St. Paul MN 55110 USA). Anthony J. M. McDaniel F. D. Reofrow S. Molecule free SIMS for semiconductors. Proc.-Electrochem. SOC. 1994,94,349. (Mater. Sci. Lab. Texas Instruments Dallas TX 75265 USA). Kunz A. K. Alstrin A. L. Casey S. M. Leone S. R. Single photon ionization laser optical probe technique for semiconductor growth.Proc. SPIE-Int. SOC. Opt. Eng. 1994 2337 20. (Joint Inst. Lab. Astrophys. Natl. Inst. Stand. Technol. Boulder CO 80309-0440 USA). Moulin C. Briand A. Decambox P. Fleurot B. Lacour J. L. Mauchien P. Remy B. Methods for analysis of actinides and radioelements of interest by laser spectroscopy. Radioprotection 1994,29 5 17. (Lab. Spect. Laser Anal. CE-Saclay 91 19 1 Gif-sur-Yvette France). Maunit B. Hachimi A. Calba P. J. Krier G. Muller J. F. New method for the determination of iron oxidation states by resonant and non-resonant ioniz- ation mass spectrometry. Rapid Commun. Mass Spectrom. 1995,9,225. (Lab. Spectrom. Masse et Chim. Laser IPEM 57078 Metz France). Schriemer D. C. Li L. Laser-induced surface ionization in a time-of-flight mass spectrometer.Rev. Sci. Instrum. 1995 66 55. (Dept. Chem. Univ. Alberta Edmonton Alberta Canada T6G 2G2). Coath C. D. Long J. V. P. High-brightness duoplasma- tron ion source for microprobe secondary-ion mass spectrometry. Rev. Sci. Instrum. 1995,66 1018. (Bullard Labs. Univ. Cambridge Cambridge UK). van der Heide P. A. W. Zhang M. Mount G. R. McIntyre N. S. Infinite velocity method new method for SIMS quantification. Surf. Interface Anal. 1994 21 747. (Western Sci. Centre Univ. Western Ontario London Ontario Canada N6A 3K7). Tomita M. Homma Y. Saito K. Secondary ion yields depending on the primary oxygen ion energy in Cameca IMS-4f instrument. Surf Interface Anal. 1994 21 864. (Res. and Dev. Center Toshiba Corp. Kawaski 201 Japan). Marie Y. Gao Y. Saldi F. Migeon H.N. Influence of the Cs concentration on the formation of MCs+ in SIMS analysis. Surf Interface Anal. 1995 23 38. (Lab. Anal. Mater. Centre Rech. Public-Centre Univ. Luxembourg L-1511 Luxembourg). Lee J. C. Kang H. J. Kim K. J. Kim Y. S. Moon D. W. Oxygen enhanced secondary ion emission of Fe and Co by TOF-SIMS and ISSIDR. Surf Sci. 1995 324,338. (Dept. Phys. Chungbuk Natl. Univ. Cheongju 360-763 South Korea). Fujiwara H. Murao N. Ichise E. Determination of calcium in steel by secondary-ion mass spectrometry (SIMS). Tetsu to Hagane 1994 80 902. (Fac. Eng. Kyoto univ. Kyoto 606-01 Japan). Bedilov M. R. Satybaldiev T. B. Khaydarov R. T. Tsoy T. G. Dovletov I. Yu. Study of ions of laser plasma obtained from the HTSC YBa2Cu307-x material. Uzb. Fiz. Zh. 1993 6 24. (Tashk GU Tashkent Ukraine). Popov V.F. Secondary ion analysis of HTSC ceramics. Vak. Tekh. Tekhnol. 1993,3 5. (St. Petersburg Russia). 9514154 95/4 15 5 9514156 9514157 9514 15 8 9514159 9514160 9514161 9514162 9514 163 95/4164 9514165 9514166 Kozlov B. N. Pilyugin I. I. Shchebelin V. G. Bulgakov A. V. Maiorov A. P. Predtechenskii M. R. Mass- spectrometric analysis of the composition and scattering rates of laser ablation products. Formation of ablation products from YBaCuO ceramics. Zh. Tekh. Fiz. 1994 64 154. (Fiz.-Tekh. Inst. im. A. F. Ioffe St. Petersburg 194021 Russia). Dorozhkin A. A. Ershov S. G. Filimonov A. V. Petrov N. N. Energy spectra for secondary-electron and secondary-ion emission with a change in the work function by adsorption. Zh. Tekh. Fiz. 1994 64 132.(St. Petersburg Gos. Tekh. Univ. St. Petersburg 195251 Russia). Maruo T. Azuma Y. Mass analysis of neutral particles using laser ionization. Jpn. Kokai Tokkyo Koho JP 07 29,538 [95 29,5381 (Cl. HOlJ37/252) 31 Jan 1995 Appl. 931176,359 16 Jul 1993; 8 pp. (Nippon Telegraph & Telephone Japan). Yamamoto M. Murayama S. Measurement techniques series of the spectroscopical society of Japan 29 spectrometry of plasmas. Japan Scientific SOC. Press Tokyo Japan 1995.280 pp. Hirano T. Daiho K. ICP emission spectrometer. Jpn. Kokai Tokkyo Koho JP 07 05,108 [95 05,108] (Cl. GOlN21/73) 10 Jan 1995 Appl. 93/144,629 16 Jun 1993; 4 pp. (Shimadzu Corp. Japan). Lauranto H. M. Kajava T. T. Salomaa R. R. E. Laser spectroscopy with sub-linewidth resolution. Appl. Phys. B Lasers Opt.1995 60 363. (Dept. Tech. Phys. Helsinki Univ. Technol. FIN-02 1 50 ESPOO Finland). Oki Y. Furukawa K. Ma& M. Trace element analysis in pure water by laser ablation atomic fluorescence spectroscopy. Bunko Kenkyu 1995,44 10. (Dept. Electr. Eng. Kyushu Univ. Fukuoka 812 Japan). Meyers D. P. Li G. Mahoney P. P. Hieftje G. M. Inductively coupled plasma time-of-flight mass spec- trometer for elemental analysis. Part 111 analytical performance. J. Am. SOC. Mass Spectrom. 1995 6 411. (Dept. Chem. Indiana Univ. Bloomington IN USA). Allott R. M. Grofesik A. Jones W. J. Mason R. S. Temporal and spatial distribution profiles of lithium atoms in low-pressure discharges by concentration- modulated absorption spectroscopy. J. Chem. SOC. Furuday Trans. 1995 91 1297.(Dept. Chem. Univ. Swanswa Swansea UK SA2 8PP). Chukhovskii F. N. Foerster E. Chang W. Z. Dirksmoeller M. Uschmann I. X-ray optics imaging of a plasma source with a concave-curved crystal using a ray-tracing and a wave-optics approach. Proc. SPIE- Int. SOC. Opt. Eng. 1994 2279 35. (X-Ray Optics Group the Max-Planck-Gesellschaft Friedrich Schiller Univ. Jena 07740 Jena Germany). Wei G.-l. Ming K.-w. Ni C. Yoke M.4. Orthogonal array design as a chemometric method for the optimiz- ation of analytical procedures. Part 5. Three-level design and its application in microwave dissolution of biological samples. Analyst (Cambridge UK) 1995 120 1115. (Dept. Chem. Natl. Univ. Singapore Kent Ridge Singapore 05 11 Singapore). Bergdahl I. A. Schiitz A. Hansson G.-A. Automated determination of inorganic mercury in blood after sulfuric acid treatment using cold vapour atomic absorption spectrometry and an inductively heated gold trap.Analyst (Cambridge UK) 1995 120 1205. (Dept. Occup. Environ. Med. Univ. Hosp. S-221 85 Lund Sweden). Shoukry A. F. Issa Y. M. Ibrabim H. Mohamed S. K. Atomic emission spectrometric determination of antazoline hydralazine and amiloride hydrochlorides and quinine sulfate based on formation of ion associates with manganese thiocyanate. Analyst (Cambridge UK) 1995 120 1211. (Dept. Chem. Fac. Sci. Cairo Univ. Giza Egypt). Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 357 R9514167 9514168 9514169 9514170 9514 17 1 9514172 9 514 173 9514174 95/41 75 9514176 9514 177 9514178 Brown J. H. Vaz J.E. Benzo Z. Velosa M. Potassium determination by slurry technique. Analyst (Cambridge UK) 1995 120 1215. (Unidad Tech. Nucl. Inst. Venezolano Invest. Cien. (IVIC) Aptdo. 21827 Caracas 1020A Venezuela). Chow P. Y. T. Chua T. H. Tang K. F. Ow B. Y. Dilute acid digestion procedure for the determination of lead copper and mercury in traditional Chinese medicines by atomic absorption spectrometry. Analyst (Cambridge UK) 1995 120 1221. (Dept. Sci. Serv. Inst. Sci. and Forensic Med. Outram Rd. Singapore 03 16 Singapore). Zybin A. Schnurer-Patschan C. Niemax K. Wavelength modulation diode laser atomic absorption spectrometry in modulated low-pressure helium plasmas for element-selective detection in gas chromatography. J. Anal. At. Spectrom. 1995 10 563. (Inst. Phys.Univ. Hohenheim Garbanstr. 30 D-70599 Stuttgart Germany). Moens L. Vanhaecke F. Riondato J. Dams R. Some figures of merit of a new double focusing inductively coupled plasma mass Spectrometer. J. Anal. At. Spectrom. 1995 10 569. (Lab. Anal. Chem. Ghent Univ. Proeftruinstr. 86 B-9000 Ghent Belgium). Vanboe H. Saverwijns S. Parent M. Moens L. Dams R. Analytical characteristics of an inductively coupled plasma mass spectrometer coupled with a thermospray nebulization system. J. .4nal. At. Spectrom. 1995 10 575. (Lab. Anal. Chem. Inst. Nucl. Sci. Univ. Ghent Proeftuinstr 86 B-9000 Ghent Belgium). Thomas C. Jakubowski N. Stuwer D. Broekaert J. A. Thermospray device of improved design for application in ICP-MS. J. Anal. At. Spectrom. 1995 10 583. (Inst. Spektrochem. Angew.Spektrosk. Postfach 10 13 52 D-44013 Dortmund Germany). Raith A. Hutton R. C. Abell I. D. Crighton J. Non- destructive sampling method of metals and alloys for laser ablation inductively coupled plasma mass spec- trometry. J. And. At. Spectrom. 1995 10 591. (Fisons Instruments Elemental Analysis Winsford Cheshire UK CW7 3BX). Outridge P. M. Evans R. D. Effect of laser parameters and tooth type on the ablation of trace metals from mammalian teeth. J. Anal. At. Spectvom. 1995 10 595. (Environ. Res. Studies Program Trent Univ. Peterborough Ontario Canada K9J 7B8). Wang J. Tomlinson M. J. Caruso J. A. Extraction of trace elements in coal fly ash and subsequent speciation by high-performance liquid chromatography with inductively coupled plasma mass spectrometry. J. Anal. At. Spectrom.1995 10 601. (Dept. Chem. Univ. Cincinnati Cincinnati OH 45221-0172 USA). Woller A. Mester Z. Fodor P. Determination of arsenic species by high-performance liquid chromatog- raphy-ultrasonic nebulization-atomic fluorescence spec- trometry. J. Anal. At. Spectrom. 1995 10 609. (Dept. Chem. and Biochem. Univ. Horticulture and Food Ind. 29-35 Villanyi H-1114 Budapest Hungary). Thomas P. Sniatecki K. Determination of trace amounts of arsenic species in natural waters by high- performance liquid chromatography-inductively coupled plasma mass spectrometry. J. Anal. At. Spectrom. 1995 10 615. (Inst. Pasteur de Lille Service Eaux Environ. 1 rue Calmette BP 245 F-59019 Lille Cedex France). Hintelmann H. Evans R. D. Villeneuve J. Y. Measurement of mercury methylation in sediments by using enriched stable mercury isotopes combined with methylmercury determination by gas chromatography- inductively coupled plasma mass spectrometry.J. Anal. 9514179 9514180 95/41 8 1 9514182 9514183 9514184 9514185 9514186 9514187 9514188 9514189 At. Spectrom. 1995 10 619. (Environ. Sci. Centre Trent Univ. Peterborough Ontario Canada K9J 7B8). Robb P. Owen L. M. W. Crews H. M. Stable isotope approach to fission product element studies of soil-to- plant transfer and in uitro modelling of ruminant digestion using inductively coupled plasma mass spec- trometry. J. Anal. At. Spectrom. 1995 10 625. (CSL Food Sci. Lab. Norwich Res. Park Colney Norwich UK NR4 7UQ). Nemet B. Kozma L. Basic investigations of nano- second laser-induced plasma emission kinetics for quantitative elemental microanalysis of high alloys.J. Anal. At. Spectrom. 1995 10 631. (Dept. Phys. Janus Pennonius Univ. 7624 Pecs Hungary). Becker S. J. Dietze H.-J. Cluster formation processes in laser and spark plasmas of rare earth oxide-graphite mixtures. J. Anal. At. Spectrom. 1995 10 637. (Zentralab. Chem. Anal. Forschungszent. Julich D-52425 Jiilich Germany). Sabsabi M. Cielo P. Quantitative analysis of copper alloys by laser-produced plasma spectrometry. J. Anal. At. Spectrom. 1995 10 643. (Inst. Mater. Inst. Natl. Res. Council Canada 75 De Mortagne Blvd. Boucherville Quebec Canada J4B 6Y4). Costa-Fernandez J. M. Pereiro-Garcia R. Sanz- Medel A. Bordel-Garcia N. Effect of plasma pressure on the determination of mercury by microwave induced plasma atomic emission spectrometry. J. Anal. At. Spectrom. 1995,10 649.(Dept. Phys. and Anal. Chem. Fac. Chem. c/Julian Claveria 8 33006 Oviedo Spain). Nolte J. Schoppenthau J. Dunemann L. Schumann T. Moenke-Blankenburg L. Coupling techniques for inductively coupled plasma optical emission spec- trometry using an array spectrometer for laser solid sampling and speciation. J. Anal. At. Spectrom. 1995 10 655. (Bodenseewerk Perkin-Elmer GmbH D-88647 Uberlingen Germany). Trassy C. C. Diemiaszonek R. C. On-line analysis of elemental pollutants in gaseous effluents by inductively coupled plasma optical emission spectrometry thermo- dynamic aspects. J. Anal. At. Spectrom. 1995 10 661. (Lab. Physico-Chim. Ind. Bt 401 Inst. Natl. Sci. Appl. de Lyon (INSA) F-69621 Villeurbanne Cedex France). Bordel-Garcia N. Pereiro-Garcia R. Fernandez- Garcia M. Sanz-Medel A.Harville T. R. Marcus R. K. Preliminary study of the role of discharge conditions on the in-depth analysis of conducting thin films by radiofrequency glow discharge optical emission spec- trometry. J. Anal. At. Spectrom. 1995 10 671. (Dept. Phys. Univ. Oviedo 33007 Oviedo Spain). Prassler F. Hoffmann V. Schumann J. Wetzig K. Comparison of depth resolution for direct current and radiofrequency modes in glow discharge optical emis- sion spectrometry. J. Anal. At. Spectrom. 1995 10 677. (Inst. Festkorper- und Werkstofforsch. Dresden eV D-01171 Dresden Germany). De Gendt S. Schelles W. Van Grieken R. Muller V. Quantitative analysis of iron-rich and other oxide- based samples by means of glow discharge mass spectrometry. J. Anal. At. Spectrom. 1995 10 681. (Dept. Chem. Univ. Antwerp Universiteitsplein 1 B-2610 Antwerp Belgium).De Gendt S. Van Grieken R. E. Hang W. Harrison W. W. Comparison between direct current and radio- frequency glow discharge mass spectrometry for the analysis of oxide-based samples. J. Anal. At. Spectrom. 1995 10 689. (Dept. Chem. Univ. Antwerp (UIA) Universiteitsplein 1 B-2610 Antwerp Belgium). 358 R Journal of Analytical Atomic Spectrometry November 1995 Vol. 10
ISSN:0267-9477
DOI:10.1039/JA995100329R
出版商:RSC
年代:1995
数据来源: RSC
|
6. |
Characterization of ionization and matrix suppression in inductively coupled ‘cold’ plasma mass spectrometry |
|
Journal of Analytical Atomic Spectrometry,
Volume 10,
Issue 11,
1995,
Page 905-921
Scott D. Tanner,
Preview
|
PDF (3064KB)
|
|
摘要:
Characterization of Ionization and Matrix Suppression in Inductively Coupled CCold' Plasma Mass Spectrometry* Journal of Analytical Atomic Spectrometry SCOTT D. TANNER SCIEX 71 Four Valley Drive Concord Ontario Canada L4K 4V8 A parametric study of plasma power and central gas flow was carried out to study the transition from normal analytical conditions to cooler plasma conditions using an inductively coupled plasma mass spectrometer having a balanced load coil. 'Cold plasma' conditions (low power and high central gas flow) permit the determination of K Ca and Fe at trace levels. The effect of changing the position of the ground reference of the load coil was investigated. Trace element ionization is consistent with thermal ionization at low electron density. Ion- molecule chemistry (charge transfer) with NO+ or 02+ may be important at the cooler plasma temperature.Suppression of analyte signals by concomitant matrix elements is partially correlated with the ionization potentials of the matrix element. If the analyte ion signals are normalized to that for NO' the suppression of signals appears to be independent of the matrix element and a modest dependence on the ionization potential of the analyte element is apparent. For high concentrations of elements of low ionization potential an additional or enhanced mechanism of ionization is evident. The onset for this enhanced ionization is sharply defined by a characteristic ionization potential near 6.0 eV. The sensitivity for trace elements does not appear to be affected by this enhanced ionization.The appearance of the enhanced ionization is made evident by a change in the ratio of the NO+ and 02+ signals. Use of cold plasma conditions for the determination of K Ca and Fe in high-purity waters and acids is evident. It appears that the method may also be used for samples having moderate salt content if the analytical protocol includes measurement of the background ions NO+ and 02+. Keywords Inductively coupled plasma; mass spectrometry; secondary discharge; matrix efect ; easily ionized element eflect The appearance of oxide ions of refractory elements was observed in the earliest reports on the performance of induc- tively coupled plasma mass spectrometry (ICP-MS).ly2 With the boundary sampling used these oxide ions could dominate over atomic ions. The appearance of polyatomic ions can compromise the determination of isobaric (having the same mass-to-charge ratio) elements.When the interference appears at the most abundant isotope of the element to be determined the analyst may have to resort to measurements at a less abundant isotope with a concomitant loss of sensitivity. Progress in the reduction of these interferences has been substantial (for example through interface design3 and the use of mixed gas plasmas4) but polyatomic ions associated with primary plasma ions remain a problem. One of the most significant of these interferences is that of ArO" with the dominant isotope of Fe+ at m/z=56. Addition of N2 to the plasma gas can substantially reduce the interference at m/z= 56 but increases the interference at the less abundant isotope 54Fe+ by ArN+.4 In addition the primary plasma ions can interfere directly with the determination of certain elements * Presented at the 1995 European Winter Conference on Plasma Spectrochemistry Cambridge UK January 8-13 1995.(e.g. 40Ar+ with 40Ca+). Even for current instruments that show high abundance sensitivity (a measure of the residual signal at 1 u lower than the mass of a dominant ion which is a limitation in mass spectral resolution) the very large signal for 40Ar+ can interfere with the dominant isotope of K+ at 39 u. In addition the measurement at m/z = 39 is also compli- cated by the presence of 38Ar1H+ and that at the other important isotope of K is interfered with by 40Ar1H+. One solution to this isobaric interference problem is to analyse the sample under high mass spectral resolution (e.g.a magnetic sector mass ~pectrometer).'>~ At a resolution of m/Am=2500 the signal for ArO+ is resolved from that for 56Fe+ at about half peak height. Where the Fe is to be determined at very low trace levels yet higher resolution is required. An alternative approach for certain elements appli- cable to quadrupole-based instruments is to operate the plasma source under conditions of lower power and higher nebulizer flow (and perhaps increased sampling depth and aerosol desolvation). This approach was first reported by Jiang et ~ 1 . ~ for the determination of K isotope ratios. They observed that under these conditions the background mass spectrum changed from one dominated by Arf species to one dominated by NO'.This opened the possibility of determining the K isotope ratios without substantial interference from Ar + or ArH+. The calibration graphs obtained under these 'cooler' plasma conditions were found to show two linear segments intersecting at about 10 mg 1-1 (10 ppm) K. This change in response was ascribed to a change in the dominant plasma ion from NO+ to K+ that is a self-induced matrix effect at about 10ppm. Appearance of a matrix effect at such low concentrations suggests that these plasma conditions may be useful only for analyses of samples having a low salt content. The correlation of the matrix effect with the change of domi- nant plasma ion also inferred that the mechanism of ionization involved ion-molecule chemistry of the plasma ion.This is distinguished from normal plasma conditions for which ana- lyte ionization is dominated by electron impact,8 with ion- molecule chemistry (charge transfer) playing a significant role only in the formation of highly excited ion^.^^^^ The original report on using 'cooler' plasma conditions ended with a caution that such results appeared to be achievable only under con- ditions where a secondary discharge between the plasma and the sampling orifice was suppressed. Subsequently Sakata and Kawabata" recognized the impor- tance of this mode of operation for the determination of K Ca and Fe by ICP-MS. The insertion of a grounded metal shield between the load coil and the torch as suggested by Gray,12 attenuated the secondary discharge.Combining the 'Shield Torch' with conditions of lower plasma power higher nebulizer flow and larger sampling depth led to the suppression of polyatomic argide ions notably ArO+. That report com- pared the spectra with and without the electrostatic shield and mapped the response of certain background and analyte ions as a function of plasma power and carrier flow. Photographs of the region between the sampler and skimmer Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 905demonstrated that the electrostatic shield suppressed the dis- charge that was otherwise present. It was noted that suppres- sion of the secondary discharge was of itself insufficient to attenuate the argide species to useful levels; operation under cooler plasma conditions was also required.Hence two sources for the argide interferences were identified (1) derived from the plasma itself (ascribed to capacitive coupling between the load coil and plasma resulting in ionization of polyatomic argides) and (2) formed within the first stage of the vacuum interface owing to the secondary discharge. Nonose et all3 studied the formation of polyatomic ions within the ICP and in the micro-plasma between the sampler and skimmer both with and without an electrostatic shield of the sort described by Gray' and by Sakata and Kawabata." Polyatomic ions were classified into two groups the first included NO' 0,' and metal monoxide ions and the second included the argide polyatomic ions. It was concluded that the former ions were characteristic of the source plasma (ICP) while the latter were formed in a secondary discharge within the vacuum interface.The dissociation equilibrium for ArX + species was consistent with a plasma temperature of 3500 K which the authors took to indicate equilibration within the vacuum interface. At about the same time Uchida and Itox4 reported that the electrostatic shield discussed above did reduce the secondary discharge but that some evidence of the discharge remained more noticeably at a plasma generator frequency of 40 MHz than at 27 MHz. They suggest that the residual secondary discharge may be responsible for the lower analyte monoxide ion signals observed at the higher frequency. In addition they note that air entrainment at large sampling depths may also lead to the formation of oxide ions of analyte species.Douglas and French'' reported that the intensity of the secondary discharge was reduced for a centre-grounded ('bal- anced') load coil configuration. This configuration may be obtained by various means including physical grounding of the load coil or using a balanced Colpitts oscillator.16 The effects of reducing the secondary discharge were claimed to include reduction in the intensity of doubly ionized species a narrowing of the kinetic energy distribution reduction of ions derived from erosion of the sampling aperture and increased orifice lifetime. This work was undertaken to evaluate the operation of an ICP-MS instrument having a balanced load coil configuration without a physical shield under 'cold' plasma conditions to permit the determination of K Ca and Fe at trace levels.In particular the signals of analyte and plasma background ions were monitored as a function of the plasma conditions (power and central channel gas flow) and of the balance of the load coil. It was furthermore the objective to characterize the effect of concomitant elements on the response of analyte and plasma ions (k the matrix effect). Analyte species which were treated as either trace elements or matrix elements in separate analyt- ical solutions were selected having a range of ionization potential mass and heat of vaporization. It was intended that characterization of the matrix effect would help to delineate the mechanism of ionization in the plasma and the importance of particle vaporization on analyte response.EXPERIMENTAL Instrumentation Experimental results were obtained on a Perkin-Elmer SCIEX Elan 6000 ICP-MS instrument. Since this instrument has not been described in the literature a schematic diagram of the major components is given in Fig. 1 and a functional descrip- tion of these components is provided below. The plasma rf generator is free-running (meaning that the Turbomolecular Turbomolecular Roughing Pump pump pump Fig. 1 Schematic diagram of the Perkin-Elmer SCIEX Elan 6000 ICP-MS system used in this work. The function and operation of the various components are described in the text frequency is automatically varied to maintain tuning) at a nominal frequency of 40 MHz. The three-turn load coil is a component of the Colpitts oscillator a schematic diagram of which is shown in Fig.2. The plasma potential (the dc potential of the plasma resulting from capacitive coupling between the load coil and plasma) is a function of the position of the ground reference along the coil as has been shown by Douglas and French." The load coil is 'balanced' (that is the position of the ground reference along the load coil is optimized) by adjustment of the capacitor plate CP1. Moving CP1 towards CP2 (referred to here as a negative displacement) moves the ground reference down the load coil away from the sampler. Therefore the plasma potential is a function of the position of CP1 and by inference the intensity of a secondary discharge can be minimized (or enhanced) by changing the displacement of CP1. For the experiments involving adjustment of the plasma potential the stand-offs that normally hold CP1 in position were removed along one edge and a threaded insulated rod was attached to this edge.The threaded rod extended through a hole drilled through the generator housing and was held in place with a nut on the outside of the generator. The position of CP1 was adjusted while the plasma was operating by adjusting the length of the threaded rod extending outside the generator housing which therefore moved the edge of CP1 attached to the threaded rod with respect to the fixed plates CP2 and CP3. Since CP1 was fixed in position along one edge this motion caused CP1 to tilt relative to the fixed plates CP2 and CP3 rather than move plane-parallel to CP2 and CP3. The capacitor position was measured as the extension of the threaded rod out of the generator housing.For all other experiments the capacitor was adjusted to give the largest ratio of Na' signal from a 10 pg 1-l (10 ppb) Na solution to background 40Ar' signal measured for a plasma power of 600 W and nebulizer flow of 1.08 1 min-l (ie. the 'cold' plasma conditions described below). This condition was also found to yield the largest Rh' signal for a plasma power of 1200 W OSCILLATOR COLPlrrS rf choke H-l Front (towards LOAD COIL Ground J- reference a s x j - POWER SOURCE Fig. 2 Schematic diagram of the Colpitts oscillator used in this work. Capacitor plate CP1 is adjustable between plates CP2 and CP3 and determines the ground reference of the load coil. Moving CP1 towards CP2 (denoted as a change in the negative direction) moves the ground reference away from the front of the load coil 906 Journal of Analytical Atomic Spectrometry November 1995 VoZ.10and nebulizer flow of 0.77 1 min-' (Le. the 'normal' plasma conditions described below). The sample was delivered at a rate of 1 ml min-l via a peristaltic pump to a cross-flow nebulizer. The double pass spray chamber was mounted outside the torch box and was maintained at ambient room temperature (about 21 "C). The resultant aerosol was not desolvated. For most experiments the entire injector (central carrier) gas flow was passed through the nebulizer (injector flow = nebulizer flow). For experiments in which ion signals were measured as a function of injector flow a constant nebulizer flow of 0.45 1 min-l was passed through the nebulizer (hence maintaining more-or-less uniform nebulization efficiency) and a make-up flow was added to the injector through a T downstream of the spray chamber; hence the total injector flow was the sum of the fixed nebulizer flow and the variable make-up flow.The nebulizer flow rate was metered using the instrument-native flow controller which was cross-calibrated using an external digital flow meter and the make-up flow (when used) was measured using an external digital flow meter. The alumina injector (central gas) tube had an id of 2 mm at its exit to the torch. The plasma (coolant) and auxiliary (intermediate) Ar flows were preset at 15 and l.Olmin-' respectively using the instrument-native flow controllers with a primary Ar input pressure of 50 psi.The sampling depth (distance from the end of the load coil to the sampler orifice) was set to 9mm and was not adjusted. The sampler ( 1.1 mm diameter orifice) and skimmer (0.88 mm diameter orifice) cones were made of nickel. The spacing between the sampler and skimmer was 6.9mm (stan- dard for this instrument). The background pressure in the interface region was about 3 Torr. The high vacuum chamber is differentially pumped by turbomolecular pumps. The higher pressure chamber (about 8 x lov4 Torr) contains the entrance ion optics. These optics consist of a grounded shadow stop at the base of the skimmer cone a cylinder lens and a grounded differential pumping aperture. The shadow stop intercepts unvaporized plasma particles preventing their deposition downstream in the ion optics.It also serves as an on-axis ground potential reference for the extracted plasma. The voltage applied to the cylinder lens is automatically tuned using the system software and is typically ramped in concert with the measured ion mass. The voltage applied to the lens is typically within the range +3 to +1OV and is found to optimize linearly with measured (transmitted) ion mass. To a first approximation the optimum lens voltage is approximately the kinetic energy that the ions gain from the supersonic expansion through the interface;17 hence the optimum linear scanning of lens voltage with meas- ured ion mass. For the 'cold' plasma conditions described below it was found sufficient to maintain the lens voltage at a constant +3 V irrespective of measured ion mass. The energy bandpass of these ion optics is narrow about 3 eV at half-height.18 This bandpass is comparable to the width of the ion energy distributions. Ions having kinetic energies signifi- cantly higher or lower than the applied lens voltage are not efficiently transmitted.Optimum sensitivity is obtained for ions having a small distribution of kinetic energies centred at the applied lens voltage. Ions created in the secondary discharge if present have substantially wider energy distributions and higher kinetic energy than those obtained from the supersonic expansion.15 Therefore these ion optics do not efficiently transmit ions that are generated in a secondary discharge. A further discussion of the ion optics can be found in ref.18. The higher vacuum chamber (about 1.5 x low5 Torr) down- stream of the differential pumping aperture contains the quadrupole mass analyser and the ion detector. The pressure in this chamber is accurately measured using a Bayert-Alpert (hot) ionization gauge tube. It is found that the analyser chamber pressure is a function of the plasma conditions as is to be expected [a cooler plasma is more dense and both the speed of sound (relevant for the flow through the sampler) and the terminal velocity (relevant for the flow through the skim- mer) are lower and so the flow through the interface is increased3]. In fact a reasonable estimate of the relative plasma temperatures for different plasma conditions can be obtained by measuring the relative analyser chamber pressure since the ratio of the zero-corrected (corrected for de-gassing) pressures is very nearly the inverse ratio of the squares of the absolute source plasma temperature^.^^'^ The mass analyser is a quadrupole mass filter with a capacitively coupled ac-only prefilter to enhance ion transport into the mass filter.The ion detector is an ETP Model AF210-Ml8E active film discrete dynode detector. A single ion impacting the surface of the first dynode yields both an analogue and a digital signal each of these having separately adjustable (automatically by the system software) gain factors. Both analogue and digital signals are simultaneously measured and archived. The system software cross-calibrates the dual signals. The digital gain channel is automatically protected against excessive ion current by hard- ware feedback shutdown circuitry.For the experiments reported here the gain of the analogue channel was set to saturate the analogue counter at 2 x lo9 ion counts s-l yield- ing a dynamic range (on the fly in a single scan) of approxi- mately 10'. Solutions The results reported here required the analysis of a number of related solutions. The distilled de-ionized water (DDIW) for background measurements and dilution was prepared in-house by distillation in glass followed by passage through a three- cartridge Millipore de-ionizer. The DDIW was usually pre- pared freshly. The background spectra reported here were obtained for 0.1% nitric acid ('Baker InstraAnalyzed' J. T. Baker Phillipsburg NJ USA) in DDIW.Analytical solutions were prepared as 10 pg I-' (10 ppb) of each analyte by serial dilution with 1 % nitric acid from 1000 mg 1-1 (ppm) standard Li Be B Na Al K Sc Fe Co Zn As Se Rh Pd Cd Sn Sb W T1 and Bi (obtained variously from SPEX Industries Edison NJ USA; Mallinckrodt Paris KY USA; Fisher Scientific Fairlawn NJ USA; and J. T. Baker Solutions). A series of matrix solutions was prepared with an additional 1 3 10 30 100 or 300mgl-' (ppm) of one of the analyte elements in the final dilution. Data are reported here for Li Na Al K Sc Zn Rh Cd T1 and Bi as the matrix elements for a total of 60 matrix solutions plus one 'clean' solution. For the experiments in which the rf generator capacitor position was varied and for those in which ion signals were measured as a function of plasma power and injector flow the analytical solution contained 10 pg 1-l (10 ppb) each of Li Be B Na Mg Sc Co As Rh Ba Ce Tb W Pb and U in 1% nitric acid.Most of these analyte elements were run separately or in groups to ensure that polyatomic interelement interferences did not occur to a significant extent over the plasma conditions studied. Also several of the more abundant isotopes were measured for each element where possible. Thermodynamic data for the elements determined as analyte ions and/or as matrix elements are given in Table 1. The elements cover a wide range of ionization potential atomic mass and heat of vaporization. It might be expected that the element is vaporized in the plasma as a molecule and that atomization follows.It may therefore be more appropriate to consider the heat of vaporization of the molecule. However the identity of the anion is not obvious (nitrate or oxide in nitric acid solution?) and the heats of vaporization of elemental nitrates and oxides do not appear to be readily available. Journal of Analytical Atomic Spectrometry November 1995 VoZ. 10 907Table 1 Thermodynamic properties of elements studied31 Element K Na Li A1 U TI sc Bi Sn Rh c o Fe W B Pd Sb Cd Be Zn Se As Mg Most abundant mass/u 39 23 7 27 238 205 45 209 116 103 24 59 56 184 11 106 121 114 9 64 80 75 Ionization potential/eV 4.339 5.138 5.39 5.984 6.08 6.106 6.54 7.287 7.342 7.46 7.644 7.86 7.87 7.98 8.296 8.33 8.639 8.991 9.32 9.391 9.75 9.81 Heat of vaporization/ kcal mol - 18.88 23.4 32.48 67.9 38.81 80.0 41.1 55.0 127.0 31.5 93.0 84.62 75.0 89.0 46.665 23.86 27.43 14.27 - - - ICP-MS Optimization modes could be obtained by loading the plasma parameter file (including plasma power gas flows and lens voltages) without further operator intervention. In the course of the parametric study presented here the plasma temperature clearly varied substantially as the plasma power and injector flow were adjusted over the wide ranges investigated.Consequently the kinetic energies that the ions gained from the supersonic expansion also varied throughout the course of the parametric experiments. As noted above optimum ion transmission is obtained when the applied lens voltage is comparable to the ion kinetic energy. Therefore the lens voltage should properly have been adjusted for each plasma condition (power and injector flow) set including the determination of the optimum mass-dependent voltage ramp.Some 78 combinations of power and injector flow were studied for each replicate of the parametric study. Even with only one lens voltage to optimize the time required for the experiment would have become prohibitive. Therefore the lens voltage was set to + 3 V throughout the parametric study. This decision holds the ramification that the ion transmission was biased towards plasma conditions yielding ion energies of the order of 3 eV which are cooler than those used under normal analytical conditions. The result is that the parametric curves are biased towards lower power and higher injector flows than they would have been had the ion lens been optimized for each condition.Two standard plasma conditions corresponding to the 'normal' analytical and 'cold plasma' conditions were adopted for most of this work. The plasma and instrumental settings used are RESULTS AND DISCUSSION indicated in Table 2. Initial optimization for the 'cold plasma' conditions was obtained by first setting the plasma power and nebulizer flows setting the lens voltage to + 3 V (fixed) and then adjusting the x-y position (horizontal and vertical pos- ition of the plasma relative to the sampling aperture) for maximum Na + signal and minimum background Ar + signal. The width of the central channel appeared to be more narrow under 'cold plasma' conditions than under 'normal' plasma conditions. These optimum 'cold plasma' operating conditions were confirmed daily.This procedure reproducibly yielded the best analytical conditions for K Ca and Fe and the sensitivity obtained for these elements was reproducible day after day. The appropriate 'cold plasma' conditions typically yielded sensitivities of the order of 1.8 x lo6 counts s-' per ppm for Fe and 30 x lo6 counts s-' per ppm for Li with continuum back- ground signals of less than 5 counts s-l and 40Ar+ (40Ca+) signals for a 0.1% nitric acid solution of less than 3000 counts s - l (less than 1800 counts s-' for DDIW); these ion signals were considered the target for appropriate optimiz- ation. The x-y optimization of the plasma relative to the skimmer as described here required no adjustment when the plasma conditions were returned for 'normal' analytical con- ditions; after set-up the 'cold plasma' and 'normal' operation Table 2 ICP-MS operating conditions Plasma rf power/W Argon gas flow rate/l min-l Plasma (coolant) Auxiliary (intermediate) Nebulizer (central channel) Sampling depth/mm Nebulizer Spray chamber Sample uptake/ml min- ' Desolvation Lens voltage Normal plasma 'Cold' plasma 1200 600 15.0 15.0 1 .o 1 .o 0.77 1.08 9.0 9.0 Cross-flow Scott-type at room temperature 1.0 None Linearly ramped + 3.0 V with ion mass +3.0 V at 7Li+ to +9.0 V at 238U+ (all ion masses) Background Spectra The mass spectrum obtained under 'normal' operating con- ditions for 0.1 YO nitric acid is shown in Fig.3(a). This spectrum was obtained following the matrix study reported below and only a cursory washout of the sample introduction system was attempted; hence some residual signals for the matrix elements Li Na Al Sc and Zn are evident.The dominant ions in the spectrum are O+ and Ar+ at m/z=16 and 40 (and the less abundant Ar+ isotopes at m/z=36 and 38). Other important ions include ArH' and the lower mass ions OH' H20+ or l80+ etc. which presumably derive from the solvent (dilute acid). Of particular note are the large background signals for Ar2+ at m/z=80 and ArO' at m/z=56. The Ar-derived ions Ar' ArH' Ar2+ and ArO+ interfere with the detection of 40Ca 39K 80Se and 56Fe the most abundant isotopes of these elements. For many applications these elements (with the exception of K) can be determined at their less abundant isotopes. In some instances desolvation or mixed gas plasmas can enhance the determination of 56Fe+.However for certain applications such as the analysis of high-purity acids for the semiconductor industry sufficiently low detection limits cannot be obtained under normal analytical conditions. The mass spectrum for the same solution obtained under 'cold plasma' conditions is shown in Fig. 3(b). The dominant background plasma ions are NO' 02+ and H30+ with most Ar-related ions greatly reduced in intensity. The very substan- tial H30 + signal is of itself a strong indication that the plasma is cool. This spectrum differs from that given in ref. 7 with the addition of important peaks in the mass range 16-20u and the persistence of ArH+ at m/z=41. These ions appear to derive from the solvent as no desolvation was used in the present work.The signal remaining at m/z = 56 is thought to be due primarily to contaminant Fe in the water and acid as its magnitude varied with the water distillation batch and with the source and concentration of the acid. This observation of variance in the background at m/z = 56 is the reason the ArO+ signal was not used as a determinant for appropriate 'cold plasma' optimum conditions. The relatively large signal at m/z=80 ascribed to ATz+ seems peculiar since the other 908 Journal of Analytical Atomic Spectrometry November 1995 Vol. 101o'O lo9 108 10' 106 lo5 lo4 lo3 lo2 r '; 10' 5 1 0 0 0 - 104,. 10-5 10' 106 lo5 lo4 lo3 lo2 10' 100 * [ej = 4 x 1 0 ~ ~ ; r = re- = 3500 A A . . . I . 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 85 Mass Fig.3 Spectra of the plasma background ions for a sample containing 0.1% HNOJ obtained under (a) the 'normal' and (b) 'cold' operating conditions given in Table2. The data were obtained using a simul- taneous dual-mode (pulse counting/analogue) detector. The analogue channel was set to saturate at 2 x lo9 counts s-'; the signals for Ar' ArH' and 0' have saturated the analogue channel for the higher power condition. Note that the vertical scales are logarithmic. Other than the plasma power and injector (carrier or nebulizer) gas flow the plasma conditions (including sampling depth sample introduction and load coil configuration) were the same for the two spectra argide ions (except for ArH') have been very substantially attenuated or eliminated. In a separate experiment this ion also showed an apparently unique dependence on spray chamber temperature.Whereas almost all the other ions (background atomic and polyatomic ions as well as analyte atomic ions) showed little variation with spray chamber tem- perature the m/z=80 ion varied by nearly two orders of magnitude over a temperature range from 0 to +44"C decreasing in intensity as the temperature was increased. It is notable also that the relative intensities of NO+ and 02' were a function of the nitric acid concentration with NO' increasing in magnitude at the expense of 02+ as the acid concentration was increased. For nitric acid concentrations below about 0.3% the increase in the NO+ signal is approxi- mately linear with acid concentration.Above this acid strength the NO' signal increases more slowly. Over the range 0.005-4% nitric acid the sum of the NO' and 02' signals remains relatively constant. It is concluded that the major source of NO+ under the experimental conditions was from the nitric acid rather than from air entrainment and that NO' derives from an ion-molecule reaction involving 02'. Finally the level of ionization in the source plasma appears to be 2-3 orders of magnitude lower under 'cold plasma' conditions relative to normal analytical plasma conditions. This con- clusion is drawn from a comparison of the total ion signals measured for the two plasmas which differ by about this magnitude (1O1O uersus 4 x lo7 s-l). With the extracted ion current reduced substantially it is to be expected that space charge effects in the ion optics are much less important.One of the effects of space charge is to reduce ion transmission efficiency,1g920 and so the ratio of the levels of ionization within the ICP is likely to be greater than the measured total ion signal ratio. Another important result of the reduction of the ion current and hence space charge is that space charge- related matrix effects should be much less significant for the 'cold plasma'. The pressure in the analyser chamber under 'normal' analyt- ical conditions was approximately 1.2 x Torr (corrected for zero-flow de-gassing) while under 'cold plasma' conditions this rose to approximately 2.3 x Torr. Taking the gas kinetic temperature of the source plasma under normal con- ditions as 5300K,21922 the ratio of pressures suggests a 'cold plasma' gas kinetic temperature of about 1450 K.This tempera- ture relates to the plasma directly in front of the sampling aperture which is extracted through the sampler. It is substan- tially lower than the dissociation equilibrium temperature for ArX' species determined by Nonose et all3 with a shielded torch configuration. This suggests that under conditions where the secondary discharge is suppressed the argide ions could derive from the source plasma rather than from within the interface. The cooler plasma temperature helps to explain the difference in lens optimization for the two plasma conditions. When the plasma temperature is cooler the mass-dependent kinetic energy gained from the expansion is less and the slope of a plot of kinetic energy uersus ion mass is smaller.22 Since the voltage applied to the lens appears to be comparable to the ion kinetic energy the reduced mass-dependence of the ion kinetic energy resulting from the cooler plasma results in a lower slope of optimum voltage with mass.For the cold plasma conditions reported here the slope was sufficiently small that a static lens voltage (+ 3 V) provided approximately optimum focusing for ions of all masses. Equilibrium ionization efficiencies for the elements have been calculated by H o ~ k ~ ~ assuming an electron density of 1015 cm-3 and ionization and electron temperatures of 7500 K. Polynomial fits of the electronic partition functions over the temperature range 1500-7000 K for most of the elements listed in Table 1 have been tabulated.24 Calculated degrees of ioniz- ation (DOI) using these partition functions extrapolated to the 7500K temperature assumed by H o u ~ ~ ~ are shown in Fig. 4 where the results are plotted against ionization potential.Similar calculations assuming that the ionization and electron temperatures are equilibrated at the gas kinetic temperature of 1450K derived above yield exceedingly low DOIs. The electron density is important in the calculation of equilibrium ion densities according to the Saha equation and reflects the rate of recombination which reduces the degree of ionization. At high electron density ( lo1' ~ m - ~ ) and low temperature 4 5 6 7 8 9 10 Ionization potentiallev Fig. 4 Degree of ionization plotted as a function of ionization poten- tial for two different plasma conditions of electron number density [e- 1 ionization temperature To and electron temperature T,-.The electronic partition functions used were taken from ref. 24 and were strictly valid only for the temperature range 1500-7000 K Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 909(1450 K) the rate of recombination is much greater than the rate of ionization and the DO1 is consequently greatly reduced. Measured values of the electron density corresponding to the 'cold plasma' conditions have not been reported. Conventional optical methods appear to be limited to electron densities above about lOI3 ~ m - ~ . Values of this magnitude have been reported low in the plasma (7 mm above the load coil) for a 1.25 kW Ar ICP at relatively high central gas flow (1.2 1 min-1)?5 A similar value has been reported for a 0.9 kW plasma at a central gas flow of 1.0 1 min-' and 5 mm above the load It may be expected that under 'cold plasma' conditions where the plasma power is substantially less than that used for the above electron density measurements the electron density will be significantly lower.Furthermore the electron and ionization temperatures are probably not equilib- rated with the gas kinetic temperature. For example under the conditions for which the electron density noted above was measured the electron and gas kinetic temperatures were found to be approximately 3500 and 2700 K re~pectively.~~ The gas kinetic temperature derived from the ratio of pressures is an average temperature for the bulk plasma and other work has shown that the ions may be concentrated in the vicinity of a vaporizing particle.27 Therefore the ionization and electron temperatures may differ significantly from the bulk gas kinetic temperature.Calculated DOIs corresponding to an electron density of only 4 x 10" cm-3 and equilibration of the ioniz- ation and electron temperatures at 3500 K are also presented in Fig. 4. The temperature was chosen assuming local equilib- rium at the ArX' dissociation temperature determined by Nonose et (note that this temperature has been applied to the ICP rather than to the vacuum interface plasma) and the electron density was chosen to yield results which mimic the ionization potential-dependence of the sensitivity data presented below.Under these conditions Fe (ionization poten- tial = 7.87 eV) is approximately 15 % ionized. For the normal plasma the flow through the skimmer is about 1 x lOI9 s - ' . ~ ~ ' For a plasma temperature of 5300 K this corresponds to a sample of about 7.2cm3 s-' from the ICP. If the electron (and ion) density in the ICP is about l O " ~ m - ~ this corresponds to an electron (and ion) flow through the skimmer of about 7 x s-'. The total measured ion current at the detector is of the order of 10" s-' suggesting an over-all transmission efficiency from the skimmer tip to the detector of about Note however that the transmission efficiency for analyte ions is better than this. A fully ionized element of mass 56 u at a concentration in the original nebulized solution of 1 ppm contributes about 1.4 x 10" ions cm-3 to the plasma (assuming a nebulization efficiency of 2% a sample uptake rate of 1 ml min-' a plasma temperature of 5300 K and uniform distribution throughout the central channel at an aerosol gas flow rate of 0.771rnin-').This sample should then yield a flow of about 10" analyte ions s-' through the skimmer. With a sensitivity of about 25 x lo6 counts s-' per ppm (for Fe') this suggests a trans- mission efficiency for Fe' ions of about 3 x and in turn suggests an improvement in transmission efficiency for analyte ions of about 300 relative to that for the background ions (i.e. a corresponding loss mechanism for the background ions). This factor of 300 is consistent with the ion current measure- ments of Gillson et aL2* downstream of the skimmer for which the measured differential U+ current for 0.04 mol U 1-' was the same as the calculated U+ current through the skimmer aperture whereas the total ion current was reduced to 6 pA from the calculated 1500 PA.If the 1 ppm Fe solution is nebulized with the same efficiency into the 'cold plasma' (1.1 1 min-' aerosol gas flow rate and plasma gas kinetic temperature of 1450K) and were 15% ionized (as calculated for an electron density of 4 x 10'O cmV3 and local thermal equilibrium of the ionization and electron temperatures at 3500 K) it would contribute about 6 x lo9 ions cm-3 to the plasma. The sensitivity observed for Fe was 1.8 x lo6 counts s-' per ppm. This corresponds to about 5% of the total ion current measured (4 x lo7 counts s-').If the transmission efficiency for Fe' is the same as for the plasma ions (i.e. if there is no preferential loss of background ions) then the total ion density in the plasma should be about (4 x 107/1.8 x lo6) x 6 x lo9 z 10" ~ m - ~ which is close to the assumed electron density. For the 'cold plasma' the increase in the operating pressure suggests that the flow through the skimmer is doubled to about 2 x loi9 s-'. For an average gas kinetic temperature of 1450K this corresponds to a sample of about 4cm3 s-l from the ICP. For an electron (and ion) density in the ICP of 4 x 1O1O cmP3 this corresponds to an electron (and ion) flow through the skimmer of about 1.6 x 10" s-'. The over-all transmission efficiency is then about 3 x approximately 300 times improved over the normal plasma.This improvement in over-all transmission efficiency may result from reduced space charge effects because the ion current is r e d ~ c e d . ~ ' . ~ ~ The transport efficiency of the analyte Fe' under 'cold plasma' conditions is then approxi- mately the same as in the normal plasma and the ratio of sensitivities (1.8 x lo6 versus 25 x lo6 counts s-' per ppm) is primarily accounted for by the reduced degree of ionization in the 'cold plasma'. These crude estimates of transmission efficiency for the cold plasma clearly depend on the assumed electron density (both for the direct calculations and for the DO1 used). It is worth noting that if the electron density and temperature are this low then the Debye radius at the skimmer is compar- able to the skimmer aperture diameter which may have important ramifications for the dynamics of ion transport through the interface.20 Parametric Study of Plasma Power and Injector Flow The variation of dominant plasma ions and trace analyte ions as a function of injector flow (with a constant 0.45 1 min-' introduced through the nebulizer) at a plasma power or 1200 W is shown in Fig.5. The Ar' signal decreases as the injector flow increases presumably reflecting the decrease in the plasma temperature owing to the translation of the normal analytical zone towards (and past) the sampling orifice. This decrease in plasma temperature is further evidenced by the increase in polyatomic argides (Ar2' ArH' and ArO') with injector flow.At very high injector flows an increase in NO+ and 02' is observed. As noted above the relative intensities of NOf and 02+ are a function of the nitric acid concentration suggesting that the dominant source of the NO' is the acid introduced with the sample. Other data presented here suggest that the change in dominant ion is a result of the cooling of the plasma with the concomitant survival (or production) of neutral molecular species including NO and 02. The various analyte ions optimize at more-or-less the same injector flow nearly independent of ionization potential or mass. There may be a trend favouring higher injector flows for lower mass ions which might reflect mass-dependent radial diffusion within the plasma.30 This effect would result in a higher density of low mass ions slightly earlier in the plasma at higher injector flow.The optimum injector flow observed for analyte ions in Fig. 5(b) is higher than the optimum indicated for 'normal' plasma conditions in Table 2. This is a direct result of having fixed the lens voltage at + 3 V for this experiment as discussed under Experimental. The uniformity of analyte ion optimiz- ation with injector flow shown in Fig. 5(b) is in contrast to the element-dependent optimization observed by Sakata and Kawabata (cJ Fig. 5 of ref. 11 obtained without the ShieldTorch). Comparison of these results indicates that the occurrence of a secondary discharge perturbs the distribution 91 0 Journal of Analytical Atomic Spectrometry November 1995 Vol. 101.2 1 .o 0.8 0.6 0.4 - 2 0.2 5 0.0 0 v) .- .- 0.0 0.4 0.5 0.6 0.7 0.8 0.9 1.0 1.1 1.2 1.3 Injector fiow/i min-' Fig.5 (a) Variation of plasma background ions with injector (carrier or nebulizer) gas flow at 1200 W plasma power. The injector flow includes 0.45 1 min-' passed through the nebulizer and an adjustable make-up flow added downstream of the spray chamber. (b) Variation of trace elemental ions under the same conditions of ions either within the plasma or during extraction; a low plasma potential has the advantage of a more uniform ioniz- ation region hence more uniform optimization. Corresponding data obtained at 600 W are given in Fig. 6. At this low plasma power there is a very clear separation of Ar-derived plasma ions (at lower injector flows) and NO+ and 02+ (at higher injector flows).The optimization of analyte species now also shows a strong dependence on injector flow with elements having higher ionization potentials or heats of vaporization appearing at lower injector flows and more easily vaporized and ionized elements appearing at higher injector flows. The correlation with plasma temperature is easy to draw but there may be an over-riding dependence for the low ionization potential elements on the concomitant appearance of NO' and 02+ as dominant plasma ions. It is possible then that the separation on the basis of ionization potential may be due to plasma temperature (thermal ionization or electron impact ionization) or it may be due to a change towards dominance of ion-molecule reaction ionization (charge transfer) of the lower ionization potential elements with NO + and 02+ as those ions become important at lower temperature.The W' ion optimizes only at lower injector flows despite having a moderate ionization potential. The heat of vaporiz- ation for W is not available. However the melting-point of W is very high (3650 K3'). It is probable that the hotter plasma conditions at lower injector flows are required to vaporize and atomize this element. Some of the elements show local maxima at both low and high injector flows. The increase in response at low injector flows for Rh+ and Co' species may reflect their relatively high heats of vaporization (the highest of those known for the suite of elements investigated). The Mg' ion also shows a minor local maximum at low injector flow.This might suggest that Mg can be vaporized as either the atom (which has a low heat of vaporization and may appear at .N 1.2 Q - E g 1.0 0.8 0.6 0.4 0.2 0.0 0.4 0.5 0.6 0.7 0.8 0.9 1.0 1.1 1.2 1.3 1.4 Injector fbwA min-' Fig. 6 (a) Variation of plasma background ions with injector (carrier or nebulizer) gas flow at 600 W plasma power. The injector flow includes 0.45 1 min-l passed through the nebulizer and an adjustable make-up flow added downstream of the spray chamber. (b) Variation of trace elemental ions under the same conditions higher injector flow rates) or as the oxide MgO (which has a high melting-point and may therefore be vaporized only at lower injector flow rates). The appearance of two local maxima (with respect to injector flow) of the same atomic analyte ion may indicate either a change of source of ionization or a change in the source of vaporization and atomization.The intermediate behaviour of Be having a high ionization poten- tial is difficult to explain. These data are comparable to the ShieldTorch data presented in Fig. 6 of ref. 11 with the import- ant addition here of the rise to dominance of NO+ and 02+ at high injector flow. Nonose et ~ 1 . ' ~ also observed the distinc- tion of the argide species from NO' and 02+ on the basis of injector (carrier) gas flow under conditions where the secondary discharge was minimized although that work was performed at higher plasma power. The variation of ion signals with plasma power at an injector flow of 1.10 1 min-' (corresponding to the 'cold plasma'injector flow) is given in Fig.7. The argide ions are important at higher plasma powers and the oxides and molecular ions at lower powers. The Ar2+ ion shows a bimodal optimization appearing at both high and low plasma power perhaps reflecting its source (Ar') at higher power but its persistence owing to less fragmentation at lower power and temperature. Again the more easily vaporized and ionized elements optimize at lower plasma powers corresponding either to lower plasma tempera- tures or to the appearance of NO' as a reactant ion. Elements having a higher ionization potential or vaporization energy appear at higher plasma powers. The behaviour of the analyte ions shown here notably the appearance of W' only at higher power and the optimization of Be+ at intermediate power correlates with their responses to injector flow in Fig.6(b). The decrease in the Ar+ signal as the injector flow is increased or the plasma power is decreased may be due to the cooling of the plasma. The increase of the polyatomic argide ions (ArO' and Ar2') at intermediate injector flow or power Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 91 1500 600 700 800 900 1000 1100 1200 1300 1400 1500 Plasma powerMl Fig.7 (a) Variation of plasma background ions with plasma power at injector (carrier or nebulizer) gas flow of 1.10 I min-l. The entire injector flow passed through the nebulizer and no make-up gas was added. (b) Variation of trace elemental ions under the same conditions may reflect the combined effects of the reduced source ions (0' and Ar') and the persistence of the polyatomic ions resulting from their reaction with Ar at the lower plasma temperature.These effects have opposite temperature depen- dence and could give rise to the appearance of the ionic species at intermediate plasma temperatures. It could be postu- lated that the appearance of NO+ and 02+ at even cooler plasma conditions is a result of the production or persistence of neutral H20 NO or 02 and their subsequent ionization by electron impact. Primary ionization of NO or 0 by electron impact may lead directly to NO+ and 02+. Primary ionization of atoms (H or 0) may be followed by ion-molecule reactions leading to the prominence of NO+ and 0,' accord- ing to H++02+02++H (k=l.l7x 10-9)32 H+ +H20-+H20+ +H (k=8.2 x O+ +H20-+H20+ +O H20+ +02+02+ +H20 H20+ + H20+H30+ +OH (k=2.3 x 10-9)33 ( k z 2 x 10-10)34 (k= 1.7 x 10-9)33 H30+ +NO +X+NO+ + H20 +XH 0,++N0-+NO++O2 ( k = 4 .5 ~ 1 0 - ~ ' ) ~ ~ 0,' +N+NO+ +O (k= 1.2 x where the known rate constants k are given in units of cm3 molecule- s- at room temperature. The reaction forming NO+ from H30+ is a two-step process involving the formation of an intermediate adduct ion and may involve a radical (X = OH 0 or H).37 These reactions have been postulated to be important in flame^^'.^^ for which the flame temperature is of the order of the 'cold plasma' temperature inferred above. The intermediates H,O+ and H30+ are observed as major ions in the 'cold plasma' mass spectrum of Fig. 3(b). Whether NO+ and 0,' are formed by primary electron impact ionization or through subsequent ion-molecule reaction chemistry the very large signal for H30+ which can only be produced by proton transfer indicates that ion-molecule chemistry does play an important role in determining the ionic composition of the 'cold plasma'.Charge transfer ionization of metal atoms by NO+ or 02+ is exothermic for atoms having ionization potentials less than those of NO or O2 (9.26436 and 12.071 eV re~pectively~~). Because these ions are molecular they have multiple internal degrees of freedom (rotation and vibration) that relax the requirement for electronic energy level resonance that charac- terizes atomic ion-atom charge transfer reactions. Therefore NO + and 0,' could behave as relatively indiscriminate charge transfer reactant ions for metal atoms.In flames however the primary source of alkali atomic ions is dissociative charge transfer with H30+ according to4' H30+ +A+A+ +H,O + H This reaction is exothermic for atoms (A) having ionization potentials less than 6.4 eV (being the difference between the ionization potential of H 13.595 eV,31 and the proton affinity of H20 7.22eV41). The importance of this reaction in flames is due in part to the preponderance of H 3 0 + . For most flames NO+ and O,+ are much less abundant and their role in elemental ionization is less well known. By direct analogy with flames it is to be anticipated that ion-molecule chemistry principally charge transfer involving H,O+ NO+ and 0,' can provide an important source of ionization for elemental atoms in the 'cold plasma'.Sensitivity Under normal plasma conditions sensitivity is a reasonably smooth function of analyte mass increasing with mass as shown in Fig. 8 where the sensitivity has been corrected for natural abundance of the isotopes. The ion density in the plasma is expected to be a function of the molarity of the solution although in ICP-MS the sensitivity is often quoted in units of mass/volume. The decrease in sensitivity at low mass is partially due to the enhanced radial diffusion of low mass analyte elements in the plasma,3o but is probably more significantly influenced by space charge effects downstream of the skimmer aperture.19i42 As can be seen in Fig. 8 sensitivity under 'cold plasma' conditions does not appear to show a strong mass dependence.The data of Fig. 8 are presented in Fig. 9 as a function of the ionization potential of the analyte elements. Significant scatter is observed for data obtained under normal plasma conditions reflecting the over-riding 0 50 100 150 200 d z Fig. 8 Sensitivity (corrected to 100% abundance) for trace elements as a function of atomic ion mass-to-charge ratio. Open circles were obtained under normal plasma conditions and filled circles were obtained under 'cold plasma' conditions 91 2 Journal of Analytical Atomic Spectrometry November 1995 Vol. 10(4 x lo1' cmd3) and ionization temperature (3500 K). In fact there is a relatively restricted range of ionization temperature and electron density that is consistent with the observed response curve assuming equilibrium thermal ionization.Assuming that elements having ionization potentials below 6 eV are completely ionized the data of Fig. 9 suggest that an element having an ionization potential of 8 eV is between 5 and 40% ionized and an element with an ionization potential of 9.5 eV is 0.02-0.5% ionized. The ionization temperatures and electron densities that would provide these degrees of ionization can be calculated. These results are presented as the four curves of Fig. 10 where the partition functions of the atom and ion have been assumed to be equal in order to simplify the calculation. The region bounded by these curves indicates the ranges of ionization temperature and electron density which could result in the observed response curve. These ranges can be further restricted by recognizing that the maximum electron density cannot exceed approximately 4 x 10l2 cm-3 (being the ratio of the total ion signals measured for the cold and normal plasmas multiplied by the known electron density of about 10'' cmT3 under normal plasma conditions).Furthermore the electron density cannot be less than about 108cm-3 being the total ion signal measured under cold plasma conditions (4 x lo7 s-l) multiplied by 10 (assuming that the transmission efficiency of the quadrupole is and that this ion flow also represents the minimum number of electrons per second extracted through the skimmer) divided by the neutral gas flow extracted from the plasma through the skimmer (about 4 cm3 s-l as derived earlier). The ionization temperature characterizing the cold plasma response curve is then in the range 2900-4400K (indicated by the shaded region of Fig.10). Again this ionization temperature range is consistent with the dissociation equilibrium tempera- ture for ArX' ions determined by Nonose et all3 It could therefore be argued either that trace element thermal ionization is approximately equilibrated at low charge density or that the mechanism of trace element ionization changes to ion-molecule charge transfer under the cooler plasma conditions. The latter mechanism can explain the bimodal optimization of several of the elements [Figs. 6(b) and 7(b)] on the basis of the change of mode of ionization. 4 5 6 7 8 9 10 Ionization potentiaVeV Fig. 9 Sensitivity (corrected to 100% abundance) for trace elements as a function of ionization potential of the trace element.Open circles were obtained under normal plasma conditions and filled circles were obtained under 'cold plasma' conditions effect of ion mass. Little explicit dependence on ionization potential is observed for normal conditions at least for ioniz- ation potentials <10eV. On the other hand the sensitivity obtained under 'cold plasma' conditions is clearly a function of ionization potential with a significant decrease in sensitivity for ionization potentials above about 8eV. It is notable that the sensitivities for T1 and Bi (high mass) are comparable to those of Li Na and K (low mass) at least within a factor of about four on a molar basis; these elements all have ionization potentials <7.5 eV. The much reduced mass bias (relative to normal conditions) supports the expectation that space charge effects should be less significant for the lower ion current condition. The improved mass bias may also derive in part from reduced radial expansion of the central channel and mass-dependent diffusion in the ICP because the plasma is cooler and sampled earlier relative to the initial radiation zone. It was observed that the sensitivity to trace elements (e.g.Fe Ca K Na and Li) under 'cold plasma' conditions was insensi- tive to the concentration of the acid at least for acid concen- trations below 1 YO. Since the relative proportions of NO' and 02' are a function of the nitric acid concentration this observation suggests that chemical ionization by charge trans- fer with NO+ is not the determinant for sensitivity or might suggest that NO' and 02+ behave equivalently as charge transfer reactant ions.Cooler plasma conditions promote the formation of polya- tomic ions notably the oxide ions of refractory elements. The sensitivity shown for Sc (45 u ionization potential = 6.54 eV) is lower by several orders of magnitude than that expected on the basis of its ionization potential partially because it appears almost exclusively as ScO'. The data given in Figs. 8 and 9 report measurements only for the atomic ion and the elements determined were chosen as being relatively poor oxide-formers. The anomalously low sensitivity to W is probably due to inefficient vaporization as discussed above and noted by others under similar conditions." Oxide or other polyatomic ions of W were not observed at significant intensity.Data given in Figs. 6(b) and 7(b) show that W is efficiently determined only under conditions yielding higher plasma temperatures (higher power and lower injector flow). For elements having ionization potentials below about 6 eV the sensitivities obtained under 'cold plasma' conditions are comparable to those obtained under normal plasma conditions. For elements having ionization potentials between 7 and 8 eV the cooler plasma conditions yield sensitivities that are up to two orders of magnitude lower and this discrepancy increases to 3-4 orders of magnitude above 9 eV. The general form of this response curve was simulated assuming equilibrium ioniz- ation in Fig. 4 for conditions of rather low electron density 4000 c C 3500 5 3000 .- w i Maximum [e-] from ratio of total ion signals I I I I *-*I __- = mi *I- ___- I ' 2500 Electron density/cm* Fig.10 Calculated ionization temperature To, and electron density [e-1 ranges that are consistent with the observed 'cold plasma' response curve assuming thermal equilibrium ionization. The curves indicate the Ton and [e-] which would result in 5 and 40% ionization of an element having an ionization potential (IP) of 8.0 eV and 0.02 and 0.5% ionization of an element having IP = 9.5 eV. The calculations assume that the electron and ionization temperatures are equilibrated. These degrees of ionization bound the observed responses shown in Fig. 9. The minimum and maximum electron densities have been derived as discussed in the text.The shaded range is consistent with the observed response curve. Because the elements having these ionization potentials are generic the electronic partition functions of the atom and ion have been assumed to be equal Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 91 3There does not appear to be a discontinuous change in sensitivity near 6.4 eV and so charge transfer with H30+ does not appear to be a dominant ionization mechanism (at the least it will not apply to elements having ionization potentials greater than 6.4eV). Charge transfer with NO+ and 0,' remains a potential source of ionization. However this ioniz- ation mechanism does not explain the change in sensitivity that occurs near 8 eV which is consistent with thermal ionization.Load Coil Ground Reference and Secondary Discharge The earlier reports on low power/high injector flow oper- ation7*11*13 have all indicated the requirement for reduction or elimination of the secondary discharge to facilitate reduction of the Ar-related background. For the instrument used in this work the plasma potential is maintained at a low level to minimize the secondary discharge under all operating con- ditions by appropriate ground-referencing of the load coil. This ground reference is determined in part by the position of the capacitor plate CP1 relative to CP2 and CP3 in the Colpitts oscillator (Fig. 2). As CP1 is moved towards CP2 the ground reference is moved along the load coil away from the front of the load coil (adjacent to the sampler orifice).Adjusting the capacitor in this manner is expected to increase the plasma potential thereby enhancing the formation of a secondary discharge. The data in Fig. 11 were obtained by adjusting the position of CP1; the position denoted '0' is that used in normal operation to minimize the secondary discharge and provide optimum sensitivity. The plasma dc potential for this position of CP1 inferred from the intercept of ion kinetic energy versus ion mass for a similar ICP-MS system (Elan 5000) is approxi- mately + 3 V.22 For that instrument which shows less discrimi- nation against high energy ions the plasma dc potential was observed to increase non-linearly with a negative displacement of CP1. At a position thought to yield a strong secondary discharge the plasma dc potential was +22 V.In the present work moving the ground reference away from the sampler (in the negative direction) results in an increase in sensitivity for Co but a larger increase in the background signals for Ar' and ArO ' . The position for optimum determination for Fe ' defined as the maximum in the ratio of Fe+ ArO' (approxi- mated as Co' ArO') is close to the '0' position. The relatively monotonic increase in signals with the change in CP1 position to negative values is abruptly discontinuous near the position marked - 10 mm. At this point all the background ion signals dramatically increase with the exception of NO' which decreases markedly in concert with the analyte ion Co' (which is typical for that of atomic elemental ions derived from the -12 -10 -8 -6 -4 -2 0 2 4 6 8 10 Capacitor positiodmm Fig.11 Analyte ion (Co') and plasma background ion (Ar+ ArOf NO+ and 02+) signals as a function of the position of the Colpitts oscillator capacitor plate CP1 (see Fig. 2) which determines the position of the ground reference along the plasma load coil sample). The data are interpreted to indicate a gradual increase in the intensity of a secondary discharge (or an equivalent effect) as the capacitor position is adjusted to move the ground reference away from the sampler with a sudden onset of a strong discharge near - 10 mm. The dramatic reduction in the signals for NO+ and Co+ at this point is probably due to a sudden change in ion kinetic energy resulting from the second- ary discharge.13 It was noted above that ion transmission through the ion optics is a strong function of ion kinetic energy with optimum transport for ions having kinetic energies comparable to the applied lens voltage.The reduction in the NO' and Co' signals probably reflects an increase in ion energies above the bandpass of the optics rather than a relative decrease in the ion densities in the plasma. At each position of CP1 an attempt was made to optimize the lens voltage for ion transmission. The optimum voltage was found to remain constant for Co' throughout the range of this experiment while that for Ar' was found to increase (from +3 to about + 6 V at the -9.5 mm position although the results reported were obtained at a constant - 3 V). The optimum lens voltage appears to be approximately equivalent to the ion kinetic energy,18 suggesting that the ion energy for Co' did not change significantly through the range of this experiment while that for Ar' did change somewhat.However the range of voltages available was limited to less than + 17 V. If the ion energy distribution was bimodal (corresponding to ions created in the source plasma and to those created in the secondary discharge) and the ion energies for ions created in the secondary discharge were above + 17 eV then these latter ions would not be effectively transmitted through the ion optics. That is the ion optics employed here discriminate against high energy ions created in a secondary discharge. Therefore the increase in the background ions near the capaci- tor position -10mm together with the decrease at that position for NO+ and Co' suggests that there was a very substantial change in the ion distribution within the sampled plasma strongly favouring argide and other background ions at this position. This effect would probably be more apparent using ion optics that did not discriminate against the higher energy ions.Concomitant Element Matrix Effect The initial publication on cooler plasma operation7 indicated a self-induced matrix suppression effect for K beginning at a concentration of 10mg 1-l (ppm). Since the total ion signal measured under 'cold plasma' conditions is significantly lower than that obtained under normal conditions it can be implied that the ion current through the skimmer tip is also less (perhaps less than the detected ion ratio as indicated above).This suggests that matrix effects resulting from space charge in the ion beam within the ion optics should be less evident. Therefore the appearance of a self-induced matrix effect at rather low concentration might provide some fundamental information regarding the ion dynamics within the plasma source. Reported here are the results of a study of matrix effects under 'cold plasma' conditions intended to provide insight into the mechanism of ionization and ion interaction within the plasma. Mass-dependent matrix effects (depending on the mass of both the analyte and the matrix elements) are expected to arise from space charge effects within the ion beam in the ion optics. Matrix effects that are a function of the ionization potentials of the analyte and matrix elements may be ascribed to ioniz- ation suppression in the plasma.When the sample is introduced as an aerosol the droplets dry to a particle before vaporization and ionization and the size of the dried particle is a function of the salt content of the sample. A matrix effect could then arise owing to incomplete vaporization of the dried particle if 91 4 Journal of Analytical Atomic Spectrometry November 1995 Vol. 10the heat transfer from the plasma is limited and this effect would depend on both the concentration and the heat of vaporization of the matrix element. There remains also the possibility of fractionation in the vaporization process whereby some elements are more readily vaporized than are others even from the same dried particle. Therefore a suite of analyte and matrix elements were selected which covered a range of mass ionization potential and heat of vaporization.Fig. 12 presents the measured ion signal (corrected for isotopic abundance) as a function of the concentration of the elements treated as concomitant elements. The data include results for the 60 different matrix solutions each including only one element at 'high' concentration (covering the range from 1 to 300 mg 1-l) plus the 'clean' 10 ppb standard solution. Since Sc was observed primarily as its monoxide ion the response for ScO' as a function of Sc concentration is given. The ion signal observed is more-or-less a function of the ionization potential of the matrix element. The response curves show two substantially linear regions.In all instances the signal is linear up to an ion signal of about lo7 counts s-'. For matrix elements having ionization potentials below 6.0 eV a second linear region having lower slope appears above about 5 x lo7 counts s-'. The intersection of these linear sections occurs near 3 x lo7 counts s-l which is approximately the ion signal observed for NO' in the blank solution (1% HNO for which NO' is the dominant ion being approximately a factor of four more intense than 02+). For matrix elements having ionization potentials above 6.0eV the slope of the second response region appears to approach zero. Fig. 13 shows normalized ion signals for trace elements as a function of the Rh' signal for solutions containing Rh as the matrix element.No clear evidence of analyte mass-dependence is apparent. In fact the trace elemental ions appear to be suppressed in a rather uniform manner. Nonetheless it is apparent that the use of a single internal standard to correct for the matrix suppression would result in significant error (of the order of a factor of three at best). All the matrices studied showed similar behaviour. The extent of suppression for a given analyte ion is a function of the concomitant matrix element. This is shown in Figs. 14 and 15 where the Co' signal is plotted against matrix concentration and matrix ion signal respectively. If the vaporization of the particle plays an important role in the matrix effect the effect should be a Molarity of matii Fig. 12 Matrix ion signals (corrected to 100% abundance) as a function of concentration of the matrix element.The data presented were obtained for 61 separate solutions comprised of six solutions each of 10 matrix elements plus the 'clean' 10 ppb standard solution. Response curves are indicated by drawing lines through the signals for the seven solutions for each of the matrix elements corresponding to concentrations of 0.01 1,3 10 30,100 and 300 ppm. The data were obtained for the most abundant atomic ion for each matrix element (with the exception of Sc for which ScO+ was measured) and were corrected for 100% natural abundance 100 - P) C .- .Q 10'' .- E E b z 10-2 10 10' Rh matrix ion signakounts s-' Fig. 13 Ion signals for trace elements (10 ppb each) as a function of Rh ion signal for solutions of different Rh concentration.The analyte ion signals were normalized to their intensities in the lowest Rh concentration 0.01 ppm 10" 1b -5 Matrix molarity 10 -2 i Fig. 14 Ion signal for Co' (added as a trace element at 10 ppb) measured for various matrix solutions as a function of matrix concen- tration. Lines are drawn through the signals obtained for the seven solutions for each of the matrix elements corresponding to concen- trations of 0.01 1 3 10 30 100 and 300 ppm l o 4 10 u lo6 10 10 * Matrix ion signallcounts s-' Fig. 15 Ion signal for Co' (added as a trace element at 10 ppb) measured for various matrix solutions as a function of matrix ion signal (corrected to 100% abundance). The data are the same as those used in Fig. 14 but are plotted here against matrix ion signal function of the matrix concentration (Fig.14) with a more severe suppression for matrix elements with high heats of vaporization (e.g. Rh and Sc). No strong correlation is observed. There is no evidence of a change in suppression for matrix elements having ionization potentials above or below that of the analyte element Co (ionization potential = 7.86 eV). The suppression of the analyte signal does not appear to correlate with the absolute ion signal measured for the various Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 91 5matrix ions (Fig. 15). The best correlation appears to be with ionization potential of the matrix element with lower ioniz- ation potential matrix elements causing more severe suppres- sion.The greater suppressions observed for Bi T1 and Rh appear to be inconsistent and may reflect a mass bias as well (although it is noted that Rh also has a high heat of vaporiz- ation which may also play a role). It remains a possibility that all of these effects are simultaneously important so that the correlation with any one is not good. As with the data of Fig. 13 the trends (or lack thereof) observed for analyte Co' with matrix ion signal were also observed for the other analyte ions. The ion signals measured for Bi' and the major background plasma ions as a function of Bi concentration are given in Fig. 16(u). The matrix ion signal increases linearly with matrix concentration then becomes non-linear and finally shows a plateau at high matrix signal. It is apparent that the matrix ion signal is anti-correlated with the background ion signals and that the non-linearity in the matrix ion response curve appears where the matrix ion signal exceeds the blank NO' signal.This cross-over might imply that NO' acts as the ionization source for Bi (ie. by charge transfer) which in turn suggests that the 'cold plasma' is dominated by ion-molecule chemistry. The similar suppression of the 02' and H20+ signals could indicate that charge transfer from these ions is also important. The H,O+ signal is expected to follow that for H20' since the latter ion is probably the primary source for proton transfer leading to H30+ (charge transfer of H,O+ with Bi is not thermodynamically allowed). Alternatively the common suppression of the background ions may indicate an approach to equilibrium with Bi' being the thermodynamically favoured terminal ion.However chemical equilibrium should result in a large difference in suppression of analyte ion signals 10 10 10 c v) 3 10 a 9 2 109 Molarity of Bi matrix element cn C .- - 108 10 7 106 105 10 -4 lo9 10" Molarity of Na matrix element 10" Fig. 16 (a) Bi' signal and dominant plasma background ion signals as a function of the concentration of Bi as a concomitant matrix element. Bi acts as a 'high ionization potential' matrix element (see text). (b) Na+ signal and dominant plasma background ion signals as a function of the concentration of Na as a concomitant matrix element. Na acts as a 'low ionization potential' matrix element for analyte elements having ionization potentials above or below that of the matrix element; this was not observed in the data of Figs.13-15. Finally the common suppression may indicate enhanced ion-electron recombination if the matrix element induces an increase in the electron density. The data shown in Fig. 16(a) were similar to those obtained for all matrix elements having ionization potentials greater than 6.0 eV. However lower ionization potential elements showed behaviour similar to that shown in Fig. 16(b) for Na as the matrix element. Here the NO' signal behaves as it did for the higher ionization potential elements but the other back- ground ions show first a modest attenuation at moderate matrix concentration (about low3 mol l-') then a recovery as the matrix concentration was increased further. The latter results argue against equilibrium amongst the background ions. For matrix elements having ionization potentials above 6.0 eV the argide ions (Ar' ArH' and ArO') behaved much as did the other trace and background ions. Typical results (obtained for Bi matrix) are given in Fig.17(u) which is analogous to Fig. 16(u). The background argide ions are sup- pressed by the concomitant matrix element although appar- ently not as severely as are NO' and the analyte ions. However for matrix elements having ionization potentials < 6.0 eV the background argide ions are significantly enhanced at high matrix concentration. The data given in Fig. 17(b) are typical of those observed for the low ionization potential matrix elements K Na and Li.For these matrix elements the argide ions are not suppressed at moderate matrix concen- tration; the initial suppression of the ArO' signal is almost certainly due to the suppression of the isobaric Fe+ (Fe was added as an analyte element at 10 ppb). Even for a K S ! Molarity of Bi matrix element .- w 107 u) E - 104 103 los5 10'~ 1 0 ' ~ lo-* Molarity of Na matrix element Fig. 17 Argide ion signals obtained as a function of matrix element concentration obtained in the same experiment as the data of Fig. 16. (a) Bi as a concomitant element. (b) Na as a concomitant element. In both instances the ArO+ signal is dominated by Fe+ added as a trace element at 10 ppb. The initial decay of the ArOf/Fe+ signal in (b) is almost certainly due to the suppression of the Fe' signal and the recovery of the signal is almost certainly due to the enhancement of the ArO' component 91 6 Journal of Analytical Atomic Spectrometry November 1995 Vol.10concentration as low as 30ppm the background signals are significantly enhanced. As noted earlier the lower ionization potential matrix elements also appear to show a second linear response region with a smaller (but non-zero) response factor beyond the concentration yielding a matrix ion signal comparable to the blank NO' signal. It is likely that this second region is a result of an additional or enhanced mechanism of ionization peculiar to matrix elements having low ionization potentials. The transition from 'high ionization potential' behaviour (sup- pression of all background ions) to 'low ionization potential' behaviour (modest suppression and then recovery of back- ground ions other than NO') occurred abruptly near an ionization potential of 6.0 eV; where A1 (ionization potential = 5.984 eV) showed substantially 'low ionization potential' behaviour TI (ionization potential = 6.1 eV) showed strictly 'high ionization potential' behaviour.The dependence has been ascribed to ionization potential rather than mass since 39K behaved strongly as a low ionization potential element and lo3Rh behaved strongly as a high ionization potential element although they differ only by a factor of about 2 in mass. C4%c (ionization potential = 6.54 eV) and 66Zn (ionization poten- tial = 9.391 eV) also appeared to show 'high ionization poten- tial' behaviour although the extent of suppression (about a factor of 3 at the highest concentrations studied) was not sufficient to be certain.] It is significant also that the ion signal obtained at high matrix concentration for some of the elements substantially exceeded the total ion signal for the blank solution.Thermal ionization of high concentrations of low ionization potential elements may substantially increase the electron density in the plasma. For example complete ionization of 30 ppm of K corresponds to an increment of 1.5 x 1014 ions and electrons per second in the plasma (assuming 2% nebuliz- ation efficiency at a sample uptake rate of 1 ml min-'). If these ions and electrons are uniformly distributed within the central channel flow the electron density would be increased by about 10l2 C M - ~ (assuming 1.1 1 min-l and a plasma temperature of 1450K).This is probably a significant enhancement in the electron density. The local plasma temperature could be increased owing to collisional heating involving the electrons accelerated in the rf field and to improved radiative transport. Miller et aE.43 discuss these effects for the dc plasma. The inversion of local electron densities by easily ionized elements (EIE) resonance absorption raises the optical absorption cross- sections for both EIE and Ar. This improves the rate of energy transport and enhances local ohmic heating. Enhancement of the electron density on-axis by the presence of 0.5 mol 1-1 Cs in the nebulized sample has been reported by Caughlin and Blades!4 Of particular interest is the report of Hanselman et u I .~ ~ specifically the data relating to the relatively cool conditions of 1.25 kW plasma power 1.2 1 rnin-l central gas flow with measurements made 7mm above the load coil. An increase in electron density on-axis was observed with the addition of 0.1 mol I-' Cs Li or Ag to the sample while the electron and gas kinetic temperatures were enhanced only for Cs (suppression was observed for Ag and no change for Li). If under 'cold plasma' conditions the plasma temperature is increased by the presence of an EIE this could then enhance thermal ionization and possibly further increase the electron density. This mechanism might explain the additional or enhanced mechanism of ionization in the presence of high concentrations of low ionization potential matrix elements.It does not however explain why most of the background ion signals increase under these conditions but NO' does not. It therefore appears that the ionization mechanism in the 'cold plasma' may involve ion-molecule chemistry in addition to thermal ionization but that there may also be an additional or enhanced mechanism of ionization at high concentrations of low ionization potential elements. It is this enhanced ioniz- ation that is responsible for the second region of linearity in the K-matrix data seen both in this work and in the original work of Jiang et aL7 The concern for analytical use is that the increase in the background signals under these conditions could confound the determination of trace elements (e.g. the determination of Fe in a sample containing a high concen- tration of a low ionization potential concomitant element for which the ArO' background signal is increased).The preceding results show that matrix suppressions are rather severe (occur at low matrix concentration) under 'cold plasma' conditions. Furthermore if the matrix element has a low ionization potential and is at sufficient concentration there is a possibility of increased interference from polyatomic background ions. Finally refractory elements form polyatomic ions (e.g. ScO' from Sc) readily under these plasma conditions and these can also interfere with trace determinations. While the application of 'cold plasma' conditions for the determi- nation of certain elements (e.g. K Ca and Fe) in ultrapure samples is clear it remains to be determined whether there is an analytical protocol that can be established to extend its application to moderate (e.g. 300ppm or less) salt content samples.As was seen in Figs. 14 and 15 an analyte ion signal (Co' in that instance) is suppressed to different extents for different matrix elements and concentrations. However it was noted that the phenomenology of Fig. 13 was duplicated for various matrix elements. As shown now in Fig. 18 the relative suppres- sion for a given analyte element in various matrices is relatively invariant. Normalization of the analyte signal (e.g. Co') to an internal standard (e.g. Rh') minimizes the dependence of the matrix effect on the identity of the matrix element although a matrix effect which is a function of the concentration of the matrix element remains.This is unlike operation under normal plasma conditions where the extent of analyte suppression and the ratio of responses for analyte ions of different masses is strongly dependent on the mass of the matrix element. Although the analyte (Co') and internal standard (Rh+) used in Fig. 18 differ in mass by only a factor of two and have similar ionization potentials the same correlation was observed for any analyte ion using any other as internal standard (provided that there was no contamination of the analyte or internal standard in the matrix solution and there was no isobaric interference). More significantly there appears to be no need to add an internal standard. Fig. 19 gives data comparable to those of Fig. 18 but using the background ion NO' as the internal standard.Clearly NO' is suppressed by the matrix in much the same manner as the analyte ions. This is to be expected if the ionization mechanism is charge transfer 1 0 ' 1 0 2 10 Rh ion SignaVcounts s-' Fig. 18 Correlation of Co' and Rh+ ion signals (both present as trace elements at 10 ppb) in different matrix element solutions at different matrix element concentrations Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 91 7J 105 c 'Y) 104 v) 3 c $ 103 cn v) C .- .- * 102 0 10' l o 4 10' l o 6 10' NO ion signallcounts s-' Fig. 19 Correlation of Co+ signal (Co was added as a trace element at 10 ppb) with the background NO' signal in different matrix element solutions at different matrix element concentrations from NO+ and the matrix effect results from suppression of the reactant ion.This conclusion requires also that charge transfer from the matrix ion is not effective at ionizing trace elements. The latter requirement is likely to hold except for resonant energy levels for which the rate constant for charge transfer between atomic species increases dramatically. The correlations of Fig. 18 and 19 are also consistent with ioniz- ation suppression resulting from enhanced ion-electron recom- bination provided that the matrix element significantly enhances the electron density. It is not clear why the data for the Sc matrix in Fig. 19 are not consistent with the data for the other matrices (it appears that the NO' signal is insufficiently suppressed since in Fig 18 the Co -t signal appears to be appropriately suppressed relative to Rh ). Under normal plasma conditions the matrix effect can be compensated by using multiple internal standards because the matrix suppression is predominantly determined by the masses of the matrix and analyte ions (although the mass-dependence is not linear).Under 'cold plasma' conditions the matrix effect is not strongly correlated with mass. However the analyte ion signal is correlated with the background NO' signal and a plot of one against the other is linear over a wide range of matrix concentrations. This is shown in Fig. 20 for a number of analyte elements in K matrix solutions of various K concentrations. The slopes of the curves differ for the different analyte elements and suggest differing rates of ion production or loss (e.g.ion-electron recombination) relative to those for NO'. The largest slopes are for Co+ Rh' and Pd' which are the elements having the largest heats of vaporization. As implied by the data of Fig. 19 the slopes are independent of the matrix element and are reasonably linear (excepting instances where the matrix standard is contaminated with the trace element). This then allows for determination of the matrix correction factor by measuring the analyte ion and NO+ responses for any acid-matched matrix solution (including an unrelated synthetic acid-matched matrix) and also its acid- matched blank. The concentration of the analyte element [MI is then given by where RFclean is the response factor (e.g.counts s-l per ppb) in a clean standard solution S(M'),ample is the ion signal for the analyte in the sample solution AS(NO+) is the difference in the NO' signals between the sample and the acid-matched - 'v) 2 ' .- cn .Q v) 3 CI 10 10' l o 5 NO ion signallcounts s-' la - E 2 10 10 10 lo-* 10" Normalized NO' signal Fig. 20 Analyte ion signals as a function of K concentration for a series of K matrix solutions. Raw signals are given in (a). The data are replotted in (b) after normalizing the signals to their intensities in the 10 ppb (clean) solution. The data of (b) allow better observation of the variation of slope with analyte element blank and is the ratio of the differences of the analyte ion and NO' signals obtained for any acid- matched matrix and blank solutions.Since the matrix suppres- sion is linear when normalized to the NO' signal the concen- tration of the matrix solution is not important but should be such as to provide substantial signal suppression (e.g. 100 ppm). From a mechanistic point of view it is notable that the trace element signals appear to be suppressed in concert with the NO' signal regardless of the ionization potential of the matrix element. In particular the trace analyte signals do not appear to be enhanced by the presence of a high concentration of a low ionization potential matrix element (cJ the linearity of analyte signals with NO' suppression in Figs. 19 and 20 combined with the apparent insensitivity of the NO + suppres- sion to conditions under which enhanced ionization is observed as shown in Figs.16 and 17). The trace element ion signals appear to follow the NO' signal rather than the other background ions or the EIE matrix signal. It is recommended that NO+ be the reference ion used for matrix correction and not some other background ion. The correlation of analyte ion signal with NO' as shown in Fig. 19 was reproducible for all the elements studied as either trace analyte or concomitant matrix. However correlation with OZ' or another background ion is not as straightfor- ward. For matrix elements having ionization potentials above 6.0eV the slope of the analyte ion versus 0,' response is relatively independent of the matrix element. However for matrix elements having ionization potentials less than 6.0 eV the correlation is not good as shown in Fig.21 in which considerable scatter in the correlation of Co' with 02' is observed for the matrix elements K Na and Li and the A1 91 8 Journal of Analytical Atomic Spectrometry November 1995 Vol. 1010' l o 5 l o 6 10' 0 ion signavcounts s-' Fig.21 Correlation of Co' signal with background 02+ signal for different matrix elements at various concentrations. The scatter observed for K Na and Li matrix solutions is a result of the initial suppression and then enhancement of the 02+ signal as the concen- tration of the matrix elements was increased. The A1 matrix data are distinctly curved reflecting the fact that the 02+ signal was not fully suppressed in these solutions data are significantly non-linear (note that these are the matrix elements having ionization potentials less than 6.0 eV).In fact this scatter arises because the 0,' is first suppressed and then recovers as the matrix concentration is increased. The distinct behaviour for A1 results because the 0,' signal did not recover at high A1 concentration but it also was not as fully suppressed as with higher ionization potential matrix elements. This difference in behaviour between low and high ionization poten- tial matrix elements is exactly analogous to the data presented in Figs. 16 and 17 above and for the same reason. As noted above it appears that there is an additional or enhanced mechanism of ionization for high concentrations of matrix elements having low ionization potentials. This enhanced ionization does not appear to affect the sensitivity to trace level analyte ions but it does affect the background plasma ion signals.Where there is a potential isobaric interference from a background plasma ion the analyst must have a means by which to identify a possible increase in the background signal. One way to do this is to determine the signals for 0,' and NO+ in the sample. Both of these ions are background ions having high signal intensity and low mass and hence are unlikely to suffer serious isobaric interference from the sample (especially since S which might interfere with 02+ has a high ionization potential and is therefore inefficiently ionized). The correlation of these ion signals as a function of matrix concen- tration for various matrix elements is shown in Fig. 22 (this is analogous to Fig.19). For matrix elements having ionization potentials greater than 6.0 eV the O,+ and NO' signals are suppressed more-or-less in unison (slope of 1). However for low ionization potential matrix elements the 0,' signal is not as suppressed as that of NO+. Other background ions includ- ing H20+ H30+ and 0' and the argide ions Ar' ArH' ArO' and AT,+ behave in a manner similar to that of 0,'. It is particularly the response of the argide ions that stimulates our concern since an increase in the ArO' background could be confused with a response for analyte Fe. The analytical protocol allowing recognition of this potential background interference is to measure the 0,' :NO+ ratio in the blank solution and in the sample (these must have the same nitric acid concentration as the NO+ signal is a function of the acid concentration).If the ratio in the sample is similar to that in the blank there is unlikely to be an enhanced background interference. Great accuracy in the measurement of this ratio is probably not required as the background increase is not significant until the ratio changes by a factor of 3 or more. As noted above the matrix element may significantly 107 .- C .- 1 0 5 lo6 10' NO ion signaVcounts s-' i ! l o B Fig. 22 Correlation of the background signals for NO+ and 0,' for different matrix elements at various concentrations. For the low ionization potential matrix elements the 02+ signal suppression does not correlate with the NO+ signal suppression. It is this behaviour for 02+ that is responsible for the scatter shown for the low ionization potential elements in Fig.21 and is taken as an indication of an additional source of ionization under these conditions increase the electron density in the plasma. If the plasma temperature (specifically the ionization and electron tempera- tures) is not concomitantly increased this will result in enhanced ion-electron recombination. Fig. 23 presents the results of calculations of ion densities in the plasma assuming that the matrix effect is one of suppressed ionization owing to enhanced ion-electron recombination. For these calculations the electron density in the absence of a matrix element was assumed to be 4 x 10" cm-3 and the ionization and electron temperatures were assumed to be equilibrated at 3500 K. For each matrix element and for each concentration the electron density was calculated assuming equilibrium thermal ionization of the matrix element (as before assuming 2% nebulization efficiency and uniform dispersal in the central channel at a gas kinetic temperature of 1450 K).The electron density is then a strong function of the concentration and ionization potential of the matrix element. Fig. 23(u) is the analogue of the experimental data given in Fig. 12. The curvature of the response curve at high matrix concentration is predicted although the ion density at which curvature is calculated to occur should be a function of the ionization potential of the matrix element rather than near the NO' signal level for the blank solution. Fig. 23(b) is the analogue of Fig.14 and predicts rather well the order of suppression of the Co' signal with matrix element. The model underestimates the suppression for T1 Bi and Rh perhaps indicating an underlying dependence of the suppression on the mass of the concomitant element which is not accounted for in the model. This mass dependence may point towards the neglect of space charge in the model or may indicate the importance of mass-dependent radial diffusion in the plasma. Fig. 23(c) shows the calculated corre- lation of analyte ion densities with NO+ density as a function of the concentration of K matrix element [cf Fig. 20(b)]. Although the model predicts a non-linear correlation for low ionization potential analyte elements the relative order of the slopes agrees with the experimental data (except for the high ionization potential analyte elements notably Cd and Zn).It is evident that the model also predicts that the relative suppres- sion (that is after normalization to either an internal standard or to NO') is independent of the identity of the matrix element as was observed experimentally in Figs. 18 and 19. The model does not account for the 'enhanced ionization' effect (increase of background ion signals and their lack of correlation with NO+ ) for the low ionization potential matrix elements. The model might be refined by including the effects of radial dispersion and non-uniformity in the plasma (particu- Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 91 910 % .% C U 10 10s 10'~ loe2 Matrix molarity 10 -' 10 -' 10" l o o Calculated normalized NO' density Fig.23 Calculated ion densities as a function of matrix element concentration assuming equiliorium thermal ionization at 3500 K and an electron density in the absence of a matrix element of 4 x 1O1O cmW3. The electron density is increased by an amount given by thermal ionization at 3500 K of the amount of matrix element introduced into the plasma and assuming uniform distribution of the electrons in the central gas flow (1.1 1 min-l) at a gas kinetic temperature of 1450 IS. (a) (b) and (c) are the calculated analogues of the experimental data given in Figs. 12 14 and 20(b) respectively larly in the vicinity of vaporizing particles) and ohmic heating resulting from the increased electron density. Nonetheless the model suggests that thermal ionization may be dominant in the plasma.CONCLUSIONS 'Cold plasma' conditions permit the determination of elements normally interfered with by Ar+ and ArO+ because the conditions suppress the appearance of Ar' and 0'. Without the source ions the polyatomic argide ions are also suppressed. The resultant plasma is dominated by NO+ and 02+ and if no attempt at desolvation is made also the water-derived ions H20+ and H30+. Under the conditions used in this work the relative proportions of NO' and 0,' are determined principally by the nitric acid concentration of the sample. Since the NO' derives from the sample it behaves as a sample species and this has importance for its use as an internal standard. Some polyatomic argide ions persist notably ArH + and Ar2+.The approach is useful only if alternate sources of excitation such as a secondary discharge are eliminated. Sensitivity under 'cold plasma' conditions appears to be primarily a function of ionization potential. The sensitivity decreases markedly above 8 eV and so the technique is most useful for elements having lower ionization potentials. Heat transfer from the plasma to the sample appears to be insufficient to vaporize elements having high heats of' vaporization. Because the cooler plasma conditions favour the formation of molecular ions (notably the oxides of refractory elements) it is important for analytical purposes also to monitor ions at 16 u below the mass of interest to account for isobaric oxide interferences. For example under the conditions used in this work 40CaO+ presents an isobaric interference for 56Fe+ which is approxi- mately 30% of the signal obtained for 40Ca+.Matrix effects under cold plasma conditions are more severe than those obtained under normal analytical conditions. The matrix effect could be consistent with a model of the plasma dominated by ion-molecule chemistry as the reactant ions notably NO+ and 02+ are suppressed by charge transfer to the matrix ion. Alternatively the matrix suppression effect is also consistent with thermal ionization as the ion signals are suppressed by ion-electron recombination enhanced by the increased electron density contributed by the matrix element. However chemical equilibrium is not achieved in the plasma as the suppression of analyte ions is not strongly correlated with ionization potentials of the elements above and below that of the matrix element.Because of the severity of the matrix effect even at low matrix concentrations (in the low ppm range) the approach is most applicable to clean waters and acids with low salt content. However the technique may also be extended to less pristine samples since much of the matrix effect can be corrected for by correlating the analyte ion response with the NO+ ion signal (or to any other sample- derived internal standard). An additional or enhanced mechan- ism of ionization appears for high concentrations of matrix elements having ionization potentials below 6.0 eV. This enhanced ionization is responsible for the change to a smaller but non-zero response factor for the matrix element when the matrix ion signal exceeds the acid-matched blank NO + signal.The additional ionization does not appear to affect the response factor for trace elements. The appearance of enhanced ioniz- ation is significant because it is accompanied by an increase in the background signals of Ar' and polyatomic ions that may interfere with the elements of interest. However the appearance of this interference is indicated by a change in the ratio of NO" to 0,'. An equivalent indicator is the ratio of NO' (or any other sample-derived internal standard) to any background ion other than NO+ (such as H20+ H,O+ or O+ or even Ar' ArH+ or Ar2+). The author is grateful to Professor R. S. Houk (Iowa State University) and Dr. John Olesik (Ohio State University) for very helpful discussions and Peter Muellerchen (SCIEX) for assistance with the Colpitts oscillator experiment.REFERENCES 1 Houk R. S. Fassel V. A. Flesch G. D. Svec H. J. Gray A. L. and Taylor C. E. Anal. Chem. 1980 52 2283. 2 Date A. R. and Gray A. L. Analyst 1981 106 1255. 3 Douglas D. J. and French J. B. J. Anal. At. Spectrom. 1988 3 743. 4 Lam J. W. and McLaren J. W. J. Anal. At. Spectrom. 1990 5 419. 920 Journal of Analytical Atomic Spectrometry November 1995 Vol. 105 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 Bradshaw N. Hall E. F. H. and Sanderson N. E. J. Anal. At. Spectrom. 1989 4 801. Moens L. Verrept P. Dams R. Greb U. Jung G. and Laser B. J. Anal. At. Spectrom. 1994 9 1075. Jiang S.-J. Houk R. S. and Stevens M.A. Anal. Chem. 1988 60 1217. Farnsworth P. B. paper presented at the 1994 Winter Conference on Plasma Spectrochemistry San Diego CA January 10-15 1994 paper IL 12. Ogilvie C. M. and Farnsworth P. B. Spectrochim. Acta Part B 1992 47 1389. Farnsworth P. B. and Omenetto N. Spectrochim. Acta Part B Sakata K. and Kawabata K. Spectrochim. Acta Part B 1994 49 1027. Gray A. L. J. Anal. At. Spectrom. 1986 1 247. Nonose N. S. Matsuda N. Fudagawa N. and Kubota M. Spectrochim. Acta Part B 1994 49 955. Uchida H. and Ito T. J. Anal. At. Spectrom. 1994 9 1001. Douglas D. and French J. B. Spectrochim. Acta Part B 1986 41 197. Douglas D. in Inductively Coupled Plasma in Analytical Atomic Spectrometry eds. Montaser A. and Golightly D. W. VCH New York 2nd edn. 1992 ch. 13. Fulford J. E. and Douglas D. J. Appl. Spectrosc. 1986 40 971. Denoyer E. R. Jacques D. Debrah E. and Tanner S. D. At. Spectrosc. 1995 16 1. Tanner S. D. Spectrochim. Acta Part B 1992 47 809. Tanner S. D. Douglas D. J. and French J. B. Appl. Spectrosc. 1994,48 1373. Barnes R. M. Crit. Rev. Anal. Chem. 1978 7 203. Tanner S. D. J. Anal. At. Spectrom. 1993 8 891. Houk R. S. Anal. Chem. 1986 58 97A. de Galan L. Smith R. and Winefordner J. D. Spectrochim. Acta Part B 1968 23 521. Hanselman D. S. Sesi N. N. Huang M. and Hieftje G. M. Spectrochim. Acta Electron. Part B 1994 49 495. van der Mullen J. A. M. Nowak S. van Lammeren A. C . A. P. Schram D. C. and van der Sijde B. Spectrochim. Acta Part B 1988 43 317. Hobbs S. J. and Olesik J. W. Anal. Chem. 1992 64 274. i993,4a 809. 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 Gillson G. R. Douglas D. J. Fulford J. E. Halligan K. W. and Tanner S . D. Anal. Chem. 1988 60 1472. Tanner S. D. Cousins L. M. and Douglas D. J. Appl. Spectrosc. 1994 48 1367. Olesik J. W. Dziewatkoski M. P. McGowan G. J. and Thaxton C. paper presented at the 1995 European Winter Conference on Plasma Spectrochemistry Cambridge UK January 8-13 1995 paper 15. Handbook of Chemistry and Physics ed. Weast R. C. CRC Press Cleveland OH 51st edn. 1970 E-74 and D-56-D60. Huntress W. T. Jr. Astrophys. J. (Suppl. Ser.) 1977 33 495. Ferguson E. E. 1973 Atomic Data and Nuclear Data Tables Academic Press New York 1973 vol. 12 p. 159. Fehsenfeld F. C. Schmeltekopf A. L. and Ferguson E. E. J. Chem. Phys. 1967,46 2802. Lindinger W. Fehsenfeld F. C. Schmeltekopf A. L. and Ferguson E. E. J Geophys. Res. 1974,79 4753. Fehsenfeld F. C. Planet. Space Sci. 1977 25 195. Debrou G. B. Goodings J. M. and Bohme D. K. Combust. Flame 1980 39 1. Goodings J. M. Bohme D. K. and Ng C.-W. Combust. Flame 1979 36 27. Huber K. P. and Herzberg G. Molecular Spectra and Molecular Structure I V Constants of Diatomic Molecules Van Nostrand Reinhold New York 1979. Hayhurst A. N. and Telford N. R. Trans. Faraday SOC. 1970 66 2784. Lias S. G. Bartmess J. E. Liebman J. F. Holmes J. L. Levin R. D. and Mallard W. G. ‘Gas-Phase Ion and Neutral Thermochemistry’ J. Phys. Chem. Reference Data 1988 17 (Suppl. l) p. 622. Turner P. J. in Applications of Plasma Source Mass Spectrometry eds. Holland G. and Eaton A. N. Royal Society of Chemistry Cambridge 1991 p. 71. Miller M. H. Eastwood D. and Hendrick M. S. Spectrochim. Acta Part B 1984 39 13. Caughlin B. L. and Blades M. W. Spectrochim. Acta Part B 1985 40 987. Paper 5/02599K Received April 24 1995 Accepted July 12 1995 Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 921
ISSN:0267-9477
DOI:10.1039/JA9951000905
出版商:RSC
年代:1995
数据来源: RSC
|
7. |
Spectroscopic method for the determination of the electron temperature in quasi-thermal air discharges. Application to an inductively coupled air plasma at atmospheric pressure |
|
Journal of Analytical Atomic Spectrometry,
Volume 10,
Issue 11,
1995,
Page 923-928
Anne-Marie Gomes,
Preview
|
PDF (689KB)
|
|
摘要:
Spectroscopic Method for the Determination of the Electron Temperature in Quasi-thermal Air Discharges. Application to an Inductively Coupled Air Plasma at Atmospheric Pressure Journal of Analytical Atomic Spectrometry ANNE-MARIE GOMES JEAN-PHILIPPE SARRETTE LYDIE MADON AND ARNAUD EPIFANIE Centre de Physique des Plasmas et de leurs Applications de Toulouse Unit2 associie au CNRS no 277 Universitk Paul Sabatier 11 8 Route de Narbonne 31 062 Toulouse Cedex France A method for the approximation of the electron temperature O in quasi-thermal air discharges based on measurements of the relative emissivities of the weakly resolved OH and NO vibrational bands in the 210-320 nm spectral range is described. The method is very sensitive and particularly suitable between 2000 and 6000 K where intensities emitted by atomic lines cannot be easily distinguished from the molecular vibrational bands.It is shown that departures from thermodynamic equilibrium induced by radiative losses or by a difference between the electron temperature O and the heavy particle temperature Og cannot lead to large systematic errors as long as the ratio X = O 0 stays below 1.2. The uncertainty of the temperature determination is discussed together with an application to an inductively coupled air plasma at atmospheric pressure. Keywords Air; inductively coupled plasma; temperature measurement; non-equilibrium In air plasmas at atmospheric pressure the dissipation of energy by heat conduction is marked by peaks in the thermal conductivity’ corresponding to the dissociation of molecular oxygen near 3500 K and molecular nitrogen near 7000 IS.Hence the temperature of air plasmas produced in direct current (dc) electric arcs or in radiofrequency (rf ) inductively coupled plasmas (ICPs) is relatively low generally under 8000 K.2,3 The energy supplied to the plasma is distributed through a very large number of excited levels atomic levels and the set of vibro-rotational levels of the electronic configur- ations of the various molecular species. The optical spectrum emitted by the plasma is therefore composed of overlapping atomic lines and molecular bands. These radiative energy losses together with the relatively inefficient energy transfer by elastic electron-heavy particle collisions can move the plasma out of local thermodynamic equilibrium (LTE).Generally the plasma can be characterized by two Maxwellian energy distribution functions one for the free electrons and one for the whole set of heavy particles associated with the kinetic temperatures 8 and 8 respectively. The determination of these two temperatures depends on the measurement of population number densities of atomic and molecular excited states. Methods based on relative rotational line intensities emitted by molecule^^-^ lead to a rotational temperature 8 that is generally assimilated to the heavy particle temperature 8,; the molecular spectra from OH NO N and N2+ are generally used. In argon discharges the electron temperature generally assimilated to excitation tem- peratures can be obtained from relative or absolute atomic line intensity measurements through Saha or Boltzmann tem- perature determinations.” In quasi-thermal air plasmas owing to the fast energy transfer between the translational motion of the free electrons and the vibrational motion of the molecules respectively characterized by 8 and 8 these two temperatures are generally assumed to be In the same way the low-lying electronic states of atoms and molecules equilibrate rapidly with the ground electronic state giving excitation temperatures O,, in agreement with 8,.The determination of these parameters cannot be performed easily. We attempted to establish an optical diagnostic method to give the electron temperature 8 which was relatively indifferent to departures from equilibrium. The method is based on a comparison between the calculated equilibrium densities of the NO and OH molecular vibrational or rotational radiative states and their measured emissivities.The previous construction of a collisional-radiative model for the air plasma taking into account radiative and collisional out-of-equilibrium processes for the ground and excited level populations was then neces- sary which allowed us to avoid the more perturbed bands and to quantify the error committed when the equilibrium is assumed. EXPERIMENTAL SET-UP AND EXPERIMENTAL STUDY The characteristics of the ICP and of the optical diagnostic device have been presented elsewhere3>I3 and are summarized in Table 1. The experimental set-up is presented in Fig. 1. The optical spectrum emitted by the (0,O) band of the A2Z-X211 transition in OH (Fig. 2) was obtained with a 100 pm entrance slit-width and with a 350 pm entrance slit-width for the (0 1) vibrational transition of the NO y system (Fig.3). The spectra were Abel transformed; some typical behaviour of the radial variations JA(r) of the NO and OH emissivities for different wavelengths (corresponding to different pixels of the photodi- ode array) is depicted in Fig. 4. The measured NO emissivities normalized by their values on the axis of the discharge JAo(r) = Jn(r)/JA(r = 0) are identical whatever the considered pixel may be. In the same way the radial evolution of the normalized area of the whole band So@) = Jn(r) dA JA(r = 0) dA s is is the same as that obtained for any of the pixels. The normalized radial evolution of the OH emissivities differs for every pixel and most of them show a maximum outside the Journal of Analytical Atomic Spectrometry November 1995 Vol.10 923J Table 1 Characteristics of the experimental set-up Inductively coupled plasma- Power supply Inductor Air-flow rate Torch R. C. Durr rf generator with tuned-line 7-turn water-cooled coil 31 mm long 11.6 1 min-' at atmospheric pressure 20 mm id quartz tube with tangential oscillator 64 MHz 2.2 kW injection Optical set-up for geometrical discharge characterization- Optics 300 mm focal length and 50 mm diameter fused-silica lens (magnification of the set-up 1 1) with a pinhole of 5 mm diameter in the image focal plane (aperture of the light beam 8 = 1") mounting; 640 mm focal length; variable entrance slit-width 1 mm height (studied area of the plasma radial direction 350 pm axial direction 1 mm) 1200 lines mm-' holographic operating in the first order; spectral resolution R = 0.031 nm per pixel (25 pm) in the spectral range 200-350 nm Photodiode array 512 pixels Hamamatsu S2304 with Peltier cooler; pixel size 25 pm width (13 pm sensitive area and 12 pm blind area) and 2.5 mm height Monochromator Jobin-Yvon HR640 Czerny-Turner Grating Detector Control of the mirror stepping motors Microcomputer tube Grating motion contrd _c__ Entrance 1 Detectors cwrtrd and data acquisition slit Diaphragm Image inversion I_ Lens system I Geometrical T scanning masma Water-cooled coil R.F.power supply 1 .o 1 0 -' J Wavelengthlnm 302 304 306 308 310 312 314 316 318 320 Fig.2 Optical spectrum emitted by the air plasma between 304 and 320 nm and observed on the axis of the discharge p 0.9 - s 0.8 - 3 c. .- 0.7 - - .E 0.6 -. E 0.5 -. 0.4 - 2 0.3 - .- &. 2 0.2 0.1 - 0 4 J 226 228 230 232 234 236 238 240 242 Wavelengthhm Fig. 1 Optical and experimental set-up axis the radial position of this maximum namely rref being independent of the pixel. CALCULATION OF THE POPULATION NUMBER DENSITIES OF THE EMITTING LEVELS The total intensity of a line of wavenumber v emitted by molecule a in electronic state T and in the vibro-rotational state characterized by the quantum numbers 21 and J during the transition from level [T 21 J ) to level [T' u' J ' ) is Fig. 3 Optical spectrum emitted by the air plasma between 227 and 242 nm and observed on a different radius of the discharge I rref r - Fig.4 Typical variations of the local emissivities J(r)OH and I The maximum emissivities obtained for OH are used to determine rref. The curve a(r) corresponds to J(r)NO J(rre& expressed14 as a function of the density of the emitting level na[T,,v,J> by where K is a constant and SJ,J and pvv are the Honl-London factors and the band strength respectively. In a non-equilibrium plasma molecular population number densities of vibro-rotational states I Z [ ~ * J > depend on the electron temperature O the heavy particle temperature O the vibrational temperature 8 and the rotational temperature Or. These densities can be calculated from the total population 924 Journal of Analytical Atomic Spectrometry November 1995 Vol.10number density na(O 0,) of species a T and gT are the energy terms and the statistical weight of the electronic state respectively Q?(Oe 0 0,) is the internal total partition function for species a and the vibrational and rotational energies G(v) and F,(J) can be expressed as a function of the usual spectroscopic constants me mexe meye ae Be Pe and De G(v) = CO,(U + f) - O,X,(V + f ) 2 + CO,Y,(U + 4)3 + . . . (3) (4) Fv(J) = BvJ(J + 1) - D,[J(J + 1)12 + . . . with B = Be - ae(v + $) and D = D + Pe(u + 3). narT,,u>(Oe 8 0 0,) of a vibrational state is then written as The molecular population number density ( 5 ) The discrete summation can be assimilated to a continuous one; if F,(J) is limited to the first order the integration gives As a first approximation and in order to interpret the emissivity measurements in terms of electron temperature the equilibrium composition for a monothermal air plasma 0 = 8 = 0 = 8 (LTE) was calculated.The different chemical species taken into account are summarized in Table2. The molecular species made by four atoms or more were not considered in this model because they dissociate at very low temperatures (@ < 2000 K). From the relative concentrations of nitrogen (78%) oxygen (21%) and argon (0.9%) in dry air and for a gas at atmospheric pressure with a 70% moisture content at 300K the population number densities ni of the 30 chemical species present were obtained by resolving the corresponding system of equations. This system is composed of 25 equations representing the ionization or attachment Q.OOE+lO I I 1 YE a.OOE+lO 7.00E+10 $ 6.00E+10 U 5 5.00E+10 f 4.OOE+lO 3.00E+10 .9 8 1.00E+10 a 0.00E+10 .- 4 2*00E+10 1000 2000 3000 4000 5000 6000 7000 8000 9000 10000 TemperatureM Fig.5 Calculated population number densities of the main radiative atomic levels or molecular electronic configurations in natural moist air at atmospheric pressure (LTE hypothesis) equilibria (Saha's law) and the dissociation equilibria (Gulberg-Waage's law); and five equations for the constraints imposed on the plasma that is the electrical neutrality the ratio between the total numbers of argon oxygen and hydrogen nuclei and the conservation of the total pressure (Dalton's law). The densities of the vibro-rotational levels and of the total rotational states are deduced from the total densities of each species using eqns.(2) and (6). The results show that below 6000 K radiation is essentially emitted from the NO and OH molecules (Fig. 5); the variations with temperature of the population number densities of the rotational levels emitting the (0-1) vibrational band of the NO y system are very fast and nearly independent in nor- malized values from the J value. The same evolution is obtained for the total population number density of the emitting vibrational level v = 0 (Fig. 6 ) . For the (0-0) transition between electronic levels A and X of OH the intensity emitted by each of the most populated rotational levels 4 < J < 15 (whose population number densi- ties are comparable) shows a maximum between 3970 and 4180 K (Table 3 and Fig.7). For the less populated levels (J > 15) maxima appear for higher temperatures. The sum- mation of all the rotational levels leads for the vibrational state u=O to a maximum at 4090K. Because of the low resolution of the measured spectra at every pixel we have superposition of lines coming from different rotational levels. This temperature was chosen as the reference temperature Qref and the corresponding radius taken as the reference radius rref. In a two-temperature plasma using the usual assumptions 8 = 0 and 8 = 0 the densities of the emitting levels can be obtained from the total densities na(O 0,) through eqn. (2) where the internal total partition function Q?(0 0 0,) can be easily expressed15 as a function of the monothermal internal total partition function Q?(Oe) (7) 0 e 0 Q?(8 O 0,) = Q?(Oe 0,) = - Q p ( 0 ) Table 2 Chemical species considered in the equilibrium model (the species considered in the collisional-radiative model are written in bold) Family Chemical species Family Chemical species Molecular nitrogen Nz Nz+ Molecular hydrogen H2 Molecular oxygen 0 2 o,+ 0 2 - Atomic oxygen 0 o+ 0- Ozone 0 3 Atomic nitrogen N N+ Atomic hydrogen H H+ Nitrogen oxide NO NO' NO- Dinitrogen oxide N 2 0 N20+ N20- Nitrogen dioxide NO2 NOz' NO2- Atomic argon Hydroxyl OH OH' OH- Nitrogen hydride NH Ar Ar' Water %O Journal of Analytical Atomic Spectrometry November 1995 Vol.10 9251 5000 6000 7000 8000 9000 10000 1000 2000 3000 4000 Temperat ure/K Fig. 6 Normalized calculated population number densities for some rotational states and for the ground vibrational state of the NO@) electronic configuration in natural moist air at atmospheric pressure (LTE hypothesis) Fig.7 Normalized calculated population number densities for some rotational states and for the ground vibrational state of the OH(A) electronic configuration in natural moist air at atmospheric pressure (LTE hypothesis) A Y = 0; B 21 = 0 J = 10; C Y = 0 ~r = 15; D Y = 0 J = 20; E Y=O J=30 Table 3 Maximum population number densities and corresponding temperature values for the OH [A u = 0 J ) rotational states J = 0-15 J = 20 and J = 30 (LTE conditions). Last column represents the total value for the OH vibrational state [A Y = 0 ) 4 5 6 J 0 1 2 3 3970 3970 3970 3970 ee/'(K) 3970 3970 3970 nOH(ee)[A,~ = O,J> 1.50 x lo8 4.45 x lo8 7.24 x lo8 9.76 + lo8 1.19 x 109 1.37 x 109 1.50 x 109 10 11 12 13 4040 4060 4090 41 10 J 7 8 9 %/(K) 3970 4020 4020 nOH(ee)[A,u = O J > 1.59 x 109 1.63 x 109 1.63 x 109 1.59 x 109 1.52 x 109 1.43 x 109 1.32 x 109 Total 4180 4420 5500 4090 J 14 15 20 30 Oe/(K) 4130 n ~ H ( e e ) [ ~ u = o,J> 1.19 x 109 1.06 x 109 4.93 x lo8 5.60 x 107 2.42 x 10" ELECTRON TEMPERATURE DETERMINATION Using the number densities calculated in the LTE conditions for the NO state [A v = 0) the ratio of the total vibrational densities nNO(oe)[A,u = O> nNO(oref1LA.u =o> P(8e) = was determined between 2000 and 6000 K (Fig.8). It is then possible to connect the radius r to the temperature 6 making P(Qe)=a(r) where a(r) is the ratio of the local emissivities measured in the discharge for the two positions r and rref JNO (r) JNO (rref) a(r) = ~ The radial evolution of the electron temperature obtained from the experimental Abel inverted proffiles for NO and OH in the rf air plasma between the central windings of the coil is shown in Fig.9. It is compared with the variations in the 926 Journal of Analytical Atomic Spectrometry November 1995 Vol. 101 1 1 1 - . - - - - . . - 10' 1 oo lo-' 1 0-2 1 o9 a lo+ 2 10-5 0 .- c 1 o4 Optically thin plasma (X = 1 .O) Optically thin plasma ( X = 1 .l) 1 o - ~ 1 o-8 1 o4 Optically thin plasma (X = 1.2) 3200 ~- 2000 3000 4000 5000 6000 Electron temperature/)< Fig. 8 Variations in the ratio P(0,) = nNo(8,)[A,U=o> &8ref)[A,o=o) calculated in natural moist air at atmospheric pressure for a LTE plasma and for a monothermal and dithermal optically thin plasma 4800 1 .%I + 3000 ~ I I I I 1 2 3 4 5 0 Radiudmm Fig. 9 Radial variations of the electronic and heavy particle tempera- tures obtained between the third and fourth windings of the coil heavy particle temperature 8 deduced from the shape of the spectra emitted by the (0-1) band of the NO y ~ystem.~ As can be seen the method is very simple and has four major advantages (i) the variation of the ratio p(6,) between 2000 and 6000 K is very fast leading to a great sensitivity in the electron temperature measurement; (ii) there is no need for high resolution; (iii) the method is based on relative intensity measurements and does not require any calibration of the detector; and (iv) departures from equilibrium caused by 100 l 5 O I 1 \ Fig.10 Uncertainty on the determination of O&). l:~Aexp(Oe)~; 2 ANo(Be) with X = 1.0; 3 AN,(8,) with X = 1.1 4 ANo(8,) with X = 1.2 radiation escape or by the non-equipartition of the kinetic energy in the plasma do not really modify the temperature determination. The influence of these effects was studied by Sarrette and c o - w o r k e r ~ ~ ~ * ~ ~ using a collisional-radiative (CR) model through the calculation in a dithermal plasma of the number densities of the emitting levels involved in eqns. (2) and (6). In the CR model more than 90 levels (ground and excited) are taken into account for the 12 chemical species written in bold in Table 2. As yet water vapour has not been included because certain reaction rate coefficients were unavailable and because of the complexity of the resolution of the coupled non-linear system of equations.We have shown that while the number densities of the emitting levels are depopulated the ratio p(6,) is nearly insensitive to departures as long as X = 8 eg remains less than 1.2 as shown in Fig. 8. Sarrette and co-workers observed that in such conditions chemical equilibria move to the highest temperatures. Shifts are generally weak for the total number densities but can be greater for the excited states. In order to analyse the effects of departures from equilibrium on the position of the emissivity maximum for the rotational states of the hydroxyl radical it was assumed that the temperature corresponding to the maxi- mum of the total number density noH was not appreciably modified from its equilibrium value with radiation and for X < 1.2.We calculated in these conditions using eqn. (2) that the positions of the maxima are only shifted for the less populated rotational states (J > 15) with no consequence on the value of the temperature Oref. DISCUSSION The uncertainty on the determination of 8,(r) can be separated into three terms = Aexp + ANO (6,) + AOH (Oe) The first term Aexp(Qe) is related to the measurement of the emissivity J N o ( r ) . We considered a *5% uncertainty on the experimental determination of p(Oe) essentially caused by the Abel transformation. As can be seen in Fig. 10 the absolute Journal of Analytical Atomic Spectrometry November 1995 Vol.10 927value of the uncertainty increases with 8 and does not exceed 60 K below 5000 K. The second term ANO(Oe) is a systematic error connected with the importance of departures from equilibrium. It is obtained from the curves in Fig. 8 and represented in Fig. 10. This error is less than +60K for X g 1.1 and 2500 K < 0 < 5000 K but cannot be ignored for X 3 1.2 and 8 < 2500 K or 8 > 5000 K. In the first case there is a strong underestimation of the electron temperature while the second case leads to its overevaluation. In order to be complete the influence of diffusive processes on p(0,) should have been taken into account. This effect generally ignored cannot be easily evaluated because of the large number of diffusing species in an air plasma.The third term represents the uncertainty on the position rref of the emissivity maximum for OH owing to the accuracy of the geometrical analysis of the plasma and the uncertainty on the corresponding temperature Oref. Although it is possible to decrease the positional uncertainty by an increase in the definition the second point is more difficult to evaluate as long as the hydroxyl radical is not taken into account in the CR model. As previously discussed this can lead to an underestimation of the electron temperature certainly less than 100 K which constitutes the largest part of A(8,) between 2500 and 5000 K. CONCLUSION A very sensitive method for the determination of the electron temperature in an air plasma at atmospheric pressure based on a comparison of the spectra emitted by the NO and OH molecules between 2000 and 6000 K is presented.There is no need for calibration of the detector and it was shown that the method was not affected by departures from thermodynamic equilibrium in the range 2500-5000 K. The authors are greatly indebted to their lamented friend Jean Bacri for kind encouragement valuable contribution and helpful discussions during the course of this work. Jean Belkheir Belhaouari is also thanked for his kind contribution. This work was supported by the ARC CNRS-ECOTECH by ADEME and by Conseil Regional Midi PyrCnCes. REFERENCES 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 Bacri J. and Raffanel S. Plasma Chem. Plasma Process. 1989 9 133. Laux C. Moreau S. and Kruger C. paper presented at the AIAA 23rd Plasmadynamics and Lasers Conference Nashville TN 1992,2969.Gomes A.-M. Bacri J. Sarrette J.-P. and Salon J. J. Anal. At. Spectrom. 1992 7 1103. Robinson D. J. Quant. Spectrosc. Radiat. Transfer 1964,4 335. Workman J. M. Fleitz P. A. Fannin H. B. Caruso J. A. and Seliskar C. J. Appl. Spectrosc. 1988 42 96. Raeymaekers B. Broekaert J. A. C. and Leis F. Spectrochim. Acta Part B 1988 43 941. Ishii I. and Montaser A. Spectrochirn. Acta Part B 1991 46 1197. Nowak S. van der Mullen J. A. M. and Schram D. C. Spectrochim. Acta Part €3 1988 43 1235. Czemichowski A. J. Phys. D 1987 20 559. Gomes A. M. J. Phys. D 1983 16 357. Park C. paper presented at the A1A.A 22nd Thermophysics Conference 1987 Honolulu HI 1987 J. Thermodynam. Heat Transfer 1989 3 253. Losev S. A. Makarov V. N. Pogosbekyan M. J. Shatalov 0. P. and Nikols’sky V. S. paper presented at the AIAA/ASME 6th Joint Thermophysics and Heat Transfer Conference Colorado Springs CO 1994. Nore D. Gomes A. M. Bacri J. and Cabe J. Spectrochim. Acta Part B 1993 48 1411. Nicholls R. W. and Stewart A. L. in Atomic and Molecular Processes ed. Bates D. R. Academic Press New York 1962 ch. 2 p. 56. Bacri J. Lagreca M. and Medani A. E’hysica 1982 113C 403. Sarrette J. P. Gomes A. M. Bacri J. Laux C. O. and Kruger C. H. J. Quant. Spectrosc. Radiat. Transfer 1995 53 125. Sarrette J. P. Gomes A. M. and Bacri J. J. Quant. Spectrosc. Radiat. Transfer 1995 53 143. Paper 5/02544C Received April 21 1995 A-ccepted June 26 1995 928 Journal of Analytical Atomic Spectrometry November 1995 Vol. 10
ISSN:0267-9477
DOI:10.1039/JA9951000923
出版商:RSC
年代:1995
数据来源: RSC
|
8. |
Application of multi-element time-resolved analysis to a rapid on-line matrix separation system for inductively coupled plasma mass spectrometry |
|
Journal of Analytical Atomic Spectrometry,
Volume 10,
Issue 11,
1995,
Page 929-933
Simon M. Nelms,
Preview
|
PDF (811KB)
|
|
摘要:
Application of Multi-element Time- resolved Analysis to a Rapid On-line Matrix Separation System for Inductively Coupled Plasma Mass Spectrometry SIMON M. NELMS AND GILLIAN M. GREENWAY" University of Hull Cottingham Road Hull North Humberside UK HU6 7RX ROBERT C. HUTTON Fisons Instruments Elemental Analysis Ion Path Road Three Winsford Cheshire UK C W7 3BX A rapid on-line matrix separation system for ICP-MS using multi-element time-resolved analysis was developed for the determination of several trace elements in complex matrix samples. A flow injection manifold was constructed consisting of a mini-column of 8-hydroxyquinoline covalently immobilized on to controlled pore glass. Analytes retained on the column were eluted using 0.1 ml of 2.0 mol I-' nitric acid. Sample volumes of 0.5 ml were analysed yielding a preconcentration factor of 5 in addition to matrix separation.The system was optimized with respect to the variables of buffer concentration buffer pH and eluent acid volume and concentration. Calibrations from both pure water and synthetic sea-water compared well and showed good linearity with correlation coefficients of 0.988-0.999 for a range of analytes. The method showed good within-run reproducibility with precisions (s,) at the 1 ng ml-l level of typically <3%. In general recoveries between 89 and 104% were obtained with the exception of Ni which showed a recovery of 78% under the compromise conditions used. The method was validated by the analysis of estuarine (SLEW-1) and coastal (CASS-2) certified reference materials. Good agreement with the certified values was obtained for both of these materials. Keywords Flow injection time-resolved analysis; inductively coupled plasma mass spectrometry on-line matrix separation immobilized 8-hydroxyquinoline Inductively coupled plasma mass spectrometry (ICP-MS) has rapidly evolved over the past decade to become one of the most sensitive accurate and reliable trace element measure- ment techniques.However the earliest experiments with ICP-MS instrumentation identified that direct analysis of samples with high levels of dissolved solids was not practical owing to rapid blockage of the sampling interface cones and/or torch injector.' The technique is generally regarded as being limited to the analysis of samples having a total dissolved solids (TDS) content of <0.2%.For some analyses this difficulty can be circumvented by dilution of the sample. This approach is not appropriate for samples such as sea-waters because of the very low levels of analyte species present in the undiluted sample. Such samples also contain matrix species which combine with the plasma gas air entrained into the plasma and solvent components leading to polyatomic spectral interferences which can seriously degrade the accuracy of the analysis. Further the presence of easily ionizable matrix elements such as Na may cause ionization suppression because of an increase in the electron density in the plasma.2 A number of procedures have been adopted to alleviate the * To whom correspondence should be addressed. Journal of Analytical Atomic Spectrometry difficulties outlined above particularly involving the separation of the trace analytes from the concentrated matrix using ion- exchange or chelating reagents.Traditionally both solvent exchange3 and batch column separation4 methods have been employed but often these procedures are time consuming and susceptible to contamination. These factors led to the develop- ment of on-line matrix separation using flow injection method- ologies. The first publication describing this approach by Olsen et ~ 1 . ~ used a column containing Chelex-100 resin incorporated into a flow injection manifold to separate pollutant elements from sea-water with subsequent detection by flame atomic absorption spectrometry (AAS). This polymer-based iminodia- cetate (IDA) ion-exchange resin is difficult to use in on-line systems because of the large volume changes that occur when it is converted from a salt form to the acid form.It also requires conditioning steps between each sample analysis which increases the analysis time. Alternative more highly cross-linked IDA resins which are less susceptible to dimen- sional changes have been employed in recent s t ~ d i e s ~ ~ but these also require conditioning between samples. The chelating reagent 8-hydroxyquinoline (8-HQ) has also been exploited in on-line matrix separation When covalently bound to a silica or controlled pore glass (CPG) support this material does not change volume with changing pH or sample composi- tion. It also possesses a reactive chelating surface which is conditioned very rapidly between samples therefore allowing a faster sample throughput.Fang and Welz" reported a rapid low sample consumption matrix separation system based on CPG-immobilized 8-HQ for the determination of heavy metals in sea-water using flame AAS detection. The use of ICP-MS as the detection system for on-line matrix separation is a more recent development. Systems using ICP-MS detection have been described by Beauchemin and Berman" and Bloxham et aL7 In both of these publications the column was incorpor- ated in the flow stream and a separate valve was used to direct the matrix to waste downstream of the column. Fang12 sug- gested incorporation of the column in the loop of a valve to allow direct switching between the sample and eluent streams circumventing the need for an additional valve.With this arrangement some matrix does pass into the detector on switching the valve but if the connecting tubing is sufficiently short the residual matrix is kept to an acceptably low level. In addition this design allows counter-current elution of retained analytes thereby yielding sharper less dispersed peaks. This paper describes a rapid on-line matrix separation system for ICP-MS using a flow injection manifold incorporat- ing a mini-column of CPG-8-HQ for the determination of several trace elements in saline samples. The column of immobi- lized chelate is located in the loop of a manual flow injection (FI) valve. The retained analytes are eluted counter-current to Journal of Analytical Atomic Spectrometry November 1995 VoE.10 929the sample flow to yield improved less dispersed FI peaks. The FI system described is based on fixed-volume injection rather than time-based sampling and gives a fivefold precon- centration in addition to the required matrix separation. The manifold design also offers very low sample consumption. Data from the transient eluted peaks have been collected using the multi-element time-resolved analysis facility supplied with the instrument. Results illustrating the effectiveness of the matrix separation process with respect to the 40Ar23Na inter- ference on 63Cu are presented together with validation of the procedure using coastal and estuarine certified reference materials. EXPERIMENTAL Reagents High-purity de-ionized water (18 MR cm resistivity Elgastat UHQ PS Elga High Wycombe Bucks.UK) was used throughout. Elemental stock solutions (1000 yg ml-' SpectrosoL BDH Poole Dorset UK) were used in the preparation of calibration solutions. The reagents 8-hydroxyquinoline 3-aminopropyltriethoxysilane and p - nitrobenzoyl chloride (Sigma Poole Dorset UK) absolute ethanol (Hayman Witham Essex UK) sodium dithionite (BDH) and concentrated hydrochloric acid (Fisons Loughborough Leicestershire UK) were used in the immobil- ization procedure. Controlled pore glass (CPG 100-125 ym particle size Fluka Gillingham Dorset UK) was used as the immobilization support. Ammonium acetate buffer (Sigma) was prepared from the solid and purified prior to use by passing through a column of Chelex-100 (Sigma) under gravity.Adjustments to pH were made using glacial acetic acid or aqueous ammonia as appropriate. The ammonia solution was prepared by isothermal distillation of concentrated aqueous ammonia (Beecroft and Partners Rotherham UK). Synthetic sea-water was prepared by dissolving sodium chloride sodium sulfate sodium hydrogencarbonate magnesium chloride cal- cium chloride and potassium chloride in water using the procedure described by van Berkel et ~ 1 . ' ~ Samples of the coastal (CASS-2) and estuarine (SLEW-1) certified reference materials (CRMs; National Research Council of Canada Ottawa Canada) were introduced to the manifold without pre-treatment. All analytical work was performed without the use of clean room facilities. Immobilization of 8-Hydroxyquinoline A modified version of the procedure described by Habib14 was used. CPG (1.0 g) was first activated by boiling in 20 ml of 10% v/v nitric acid for 30min.The product was filtered and dried in an oven at 80°C and subsequently silanized by reaction with 10 ml of 10% v/v 3-aminopropyltriethoxysilane in anhydrous toluene for 15min at room temperature. The silanized product was oven dried and reacted with a solution of 10% m/v p-nitrobenzoylchloride in chloroform for 24 h at room temperature. The product was filtered oven dried at 50°C and further treated with a 10% m/v aqueous boiling solution of sodium dithionite for 30min to reduce the nitro group to the amine. The reduced product was again filtered and dried at 50°C. This product was added to hydrochloric acid ( 5 ml 2 and reacted with sodium nitrite (4 ml 2% m/v in water dropwise addition) at 0°C to yield the diazonium salt.Finally the product was rapidly filtered and added to a solution of 8-hydroxyquinoline (20 ml 2% m/v in absolute ethanol). In this step the CPG developed a deep red colour indicating that the diazo compound had been formed and hence the immobilization had been successful. The final product was filtered washed with hydrochloric acid (2 moll-') and water and stored in a vacuum desiccator. Instrumentation ICP-MS measurements were made using a Fisons Instruments PlasmaQuad 2 Plus. The instrument was calibrated and optim- ized prior to operation using a tune solution containing the elements Be Mg Co Y La Eu and Bi at 10ngml-' in a matrix of 5% nitric acid.The transient analyte peaks were monitored using the time-resolved analysis mode. Data acqui- sition and instrument operating parameters are given in Table 1. ICP optical emission spectrometric (OES) measure- ments were made using a Perkin-Elmer Plasma 40 instrument. The instrument operating parameters are given in Table 1. Data output from the ICP was recorded using a chart recorder (BBC Servoscript Croydon Surrey UK). Matrix Separation Manifold The matrix separation manifold is illustrated in Fig. 1. It was designed to facilitate rapid processing to increase the sampling frequency. The immobilized 8-HQ was contained within a glass mini-column (2 cm x 3 mm id.) (Omnifit Cambridge UK) incorporated in the loop of a manual four-way injection valve (Rheodyne Model 5020 Supelco Poole Dorset UK).All the manifold connections were made using 0.8 mm id. PTFE tubing. The reagents were pumped at l.Omlmin-' using a peristaltic pump (Gilson Minipuls 3 Anachem Luton UK) resulting in a matrix separation floiw rate of 2.0 ml min-l and an elution flow rate of 1.0 ml min-I. Table 1 Operating parameters for the ICP and ICP-MS instruments ICP instrument- Aerosol gas flow rate -0.75 1 min-' Intermediate gas flow rate 0.6 I min-l Outer gas flow 12 1 min-' Nebulizer Cross-flow Spray chamber Ryton Emission wavelength for Mn Chart recorder settings Forward power 1350 W Reflected power ow Aerosol gas flow rate Intermediate gas flow rate Outer gas flow rate Nebulizer Spray chamber ICP data acquisition- 257.610 nm 2 V f.s.d. 1 cm min-l ICP-MS instrument- 0.939 1 min-l 1.0 1 min-' 13.0 1 mm-' De Galan type Glass water cooled 10°C Time-resolved analysis peak-jumping parameters- Time per slice 1.00 s Points per peak 3 Detector mode Pulse counting Number of selected isotopes 13 Selected isotopes (ICP-MS)- 48Ti 51V 55Mn 59C0 60Ni 63Cu 64Zn 65Cu Io7Ag 11'3Cd 1151n 140Ce 208pb Eluent loop (0.1 ml) Sample loop (0.5 ml) 1 I A 21' Waste Fig.1 Flow injection manifold 930 Journal of Analytical Atomic Spectrometry November 1995 Vol. 10Matrix Separation Procedure For matrix separation the first valve ( 1) (Fig. 1) served as the sample injection port and the second (2) as the acid eluent port. The third valve (3) allowed matrix species unretained by the column to run to waste during the separation process while aspirating water into the ICP-MS.On elution valve 3 served to direct the eluted analytes into the ICP-MS. The sample and eluent streams flowed in opposite directions through the column thereby yielding sharper eluted peaks. Cross-contamination was minimized by constructing the eluent and sampling streams separately from each other. In addition to on-line matrix separation the manifold also gave a fivefold preconcentration. Determination of Exchange Capacity The capacity of the immobilized 8-HQ was determined for Mn by both a batch and a dynamic method using ICP-OES detection. Batch determination A solution of Mn (20 pg ml-') was prepared in ammonium acetate buffer (0.1 mol dm-3 pH 6.0) and added to 0.05 g of dry immobilized 8-HQ. The mixture was equilibrated with stirring overnight.The solution was filtered and the concen- tration of Mn in the supernatant liquid was measured versus the original concentration. The decrease in the concentration of Mn was used to evaluate the capacity using the equation where C is the capacity (mmol g-') ci and cf are the concen- trations of the metal before and after equilibrium respectively (pg ml-I) M is the relative atomic mass of the metal and v is the volume of solution (ml) equilibrated with a mass m (g) of immobilized chelate. Dynamic determination The flow injection manifold was coupled to an ICP-OES instrument equipped with a chart recorder. Aqueous solutions of Mn were prepared in the range 0-700 pg ml-'. Dry immobi- lized 8-HQ (0.04 g) was packed into a glass mini-column. It was necessary to operate the manifold with an ammonium acetate buffer concentration of 2 moll-' because of the high acidity of the Mn solutions arising from the original stock solution.Nitric acid (2.0 moll-') was used as the eluent. Three repeated analyses were made at each concentration and the results were evaluated in terms of the eluted peak height. The concentration beyond which no further increase in peak height was obtained was deemed to represent the dynamic capacity limit. The dynamic capacity was evaluated using the equation where Cd is the dynamic capacity (mmol g-') c is the concen- tration of the metal at the dynamic capacity limit (pgml-') us is the volume of sample injected (ml) m is the mass of immobilized chelate in the column (8) and M is the relative atomic mass of the metal under study. RESULTS AND DISCUSSION Manifold Design The manifold developed for the project incorporated several design features to simplify and improve the matrix separation procedure.To make the method more rapid and more economi- cal in terms of sample consumption a small sample volume was utilized. To shorten the analysis time further CPG- immobilized 8-HQ was selected as the chelating reagent because column washing and conditioning could be achieved very rapidly between samples compared with iminodiacetate resins. As polymeric-based chelating resins are subject to volume changes between matrix separation and elution the dimen- sionally stable material CPG was selected as the support. This material can also be readily functionalized because of reactive silanol groups on its surface to yield useful insoluble ion-exchangelchelating reagents.The application of counter- current matrix separation and elution yielded sharper transient peaks and avoided compacting the column material at one end of the column thereby reducing the risk of back-pressure still further and ensuring good flow stability. Optimization of the Matrix Separation Procedure The procedure was optimized with respect to the parameters of buffer concentration buffer pH and eluent acid volume and concentration using a univariate approach. Eluent volumes below 0.1 ml yielded badly dispersed peaks giving poor reproducibility and volumes greater than 0.1 ml gave a lower preconcentration factor. For these reasons an eluent volume of 0.1 ml was selected.The complete optimum conditions are given in Table 2. The response of the column to selected analytes with chang- ing buffer pH is shown in Fig. 2. As the optimum buffer pH for matrix separation varies between elements a compromise pH must be selected for multi-element analysis. On the basis of the element responses illustrated in Fig. 2 pH 6.0 was chosen as values below this gave decreased retentions of some analytes. Values above this level gave lower buffer capacities (up to pH 8) and beyond pH 8 gradual hydrolysis of the CPG-based chelating material would occur. The effect of the ammonium acetate buffer concentration on the retention of the selected elements is illustrated in Fig. 3. Samples were prepared by spiking a synthetic sea-water solu- tion with the selected analytes followed by acidification with one drop of concentrated nitric acid.Acidification was per- formed in accordance with the accepted procedure of main- taining the sample integrity with respect to the trace metal content. The results in Fig. 3 show that the buffering process Table 2 Optimum conditions for on-line matrix separation ~~~ Buffer conditions Matrix separation flow rate Elution flow rate Nitric acid eluent concentration Total analysis time 4 min Ammonium acetate 0.05 mol l-' pH 6.0 2.0 ml min-' 1.0 ml min-' 2.0 moll-' (0 F A C E f Y % 2 B a I I I 3.5 4.5 5.5 6.5 7.5 8.5 Fig. 2 D Mn; E Ag; and F Ce Effect of ammonium acetate buffer pH A Pb; B Ni; C Cu; Journal of Analytical Atomic Spectrometry November 1995 Vol.10 93114 r I 12 n C D F G B E l w .A 0 0.02 0.04 0.06 0.08 0.1 0 Buffer concentratiodmol I-' 1 I I I I Fig.3 Effect of ammonium acetate buffer concentration A Ni; B Cu; C Mn; D Ce; E Ag; F V; and G Ti is effective at a minimum concentration of 0.05 moll-l. As the optimum matrix separation pH is more than 41 pH unit away from the buffer pK the buffer capacity is significantly lower than the maximum at pH 4.76.l' With decreasing buffer concentration this leads to a decrease in both the analyte percentage retention and the measurement precision. The anomalous result observed for 48Ti is due to ionogenic retention of 48Ca at low buffer concentrations. In the presence of buffer ionogenic retention of matrix species is reduced. This effect is also slightly evident at zero buffer concentration for 63Cu and 51V because of the formation of 40Ar23Na and 35C1160 in the plasma with residual Na and C1 respectively.The effect on analyte elution of increasing eluent acid concentration is illustrated for selected analytes in Fig. 4. In this study quantitative elution was observed for all the elements investigated at an acid concentration of 2.0 molle1. The acid concentration required for each individual ele- ment increased with increasing formation constant of the element-8-HQ complex. Acid concentrations greater than 2.0 moll-1 were not investigated as these would risk degrading the column and shortening its working life. To determine the effect on the column of repeated exposure to the acid eluent a second column was prepared from the same batch of immobilized 8-HQ and the two columns were compared in terms of element recoveries (Table 3).Recoveries for the selec- ted analytes were evaluated by spiking a synthetic sea-water sample with the selected elements at 10 ng ml-l. Five repeated analyses were made using the optimized manifold conditions I 1 I I 0 0.5 1 .o 1.5 2.0 Acid concentration/moI I-' Fig. 4 Effect of nitric acid eluent concentration A Pb; B Ni; C Cu; D Ag; and E V Table 3 Recovery comparison between aged and fresh columns Column Mn c o Ni c u Ce Aged column (YO) 98 99 72 91 89 Fresh column (YO) 101 104 78 95 95 and the recoveries were evaluated against a 50 ng ml-l multi- element solution prepared in 2.0 nitric acid injected into the manifold with the column by-passed. Recoveries between 89 and 104% were obtained (Table 3).The results showed that the original column performance was not signifi- cantly reduced for the analytes measured after use for approxi- mately 300 h. Dynamic and Batch Column Capacity Evaluations Evaluation of the capacity of the immobilized 8-HQ material was performed using Mn. A batch capacity of 0.086 & 0.009 mmol g - was measured. This compared well with a dynamic capacity measurement of 0.113+_0.003 mmol g-l which is in contrast to previous obser- vations of decreased capacity with dynamic ~peration.~ This illustrates that under the conditions of dynamic operation used in this study the column retains this analyte rapidly. These capacity values are consistent with earlier reported values for this material.4.9i16 The capacities with respect to other elements have not been investigated but on the basis of recovery results it is evident that the capacity of the material is sufficient for a wide range of elements.Evaluation of the Effect of Residual Matrix Species To evaluate the influence of residual matrix on the column following matrix separation and column washing the isotope ratio of 63Cu to 65Cu was evaluated for a spiked pure water sample a spiked sea-water sample and for both CRMs. If residual sodium was present at an unacceptably high level this ratio would be greater than the natural ratio because of the formation of the 40Ar23Na interference. Table 4 illustrates that residual matrix does not Significantly affect the isotope ratio measurement and therefore does not degrade the accuracy of the measurement.The accepted 63Cu 65Cu ratio is greater than the ratios measured in this study.17 This is primarily due to mass discrimination effects arising from the detector dead time (leading to lower count detection at higher count rates) and mass bias due to sequential scanning of the transient analyte peak. Calibration and Analysis of CRMs Using ICP-MS linear calibrations were obtained over the range 0-10ngml-l for analytes in both spiked pure water Table 4 Measured isotope ratio of 63Cu to "Cu for pure and saline water samples Measured 64Cu:65Cu ratio Sample description (n = 5)* Natural 63Cu 65Cu ratio accepted Cu in 5% HNO (10 ng rnl-l) Cu in sea-water (10 ng ml-l) 2.24 2.29 k 0.06 9.77 & 2.18 value" direct aspiration continuous aspiration 5.3 1 & 0.79 2.19 & 0.09 Cu in sea-water 110 ng ml-') injected Cu in 2 moll-' HNO (50 ng mI-l) injected Cu matrix separated from spiked pure Cu matrix separated from spiked sea- CASS-2 Cu ratio (1.5% salinity) SLEW-1 Cu ratio (3.5% salinity) 2.21 k0.05 2.18k0.08 2.19 4 0.06 2.16 k 0.08 water ( 5 ng ml-l) water ( 5 ng rn1-I) matrix separated matrix separated ~- * Values quoted with uncertainty (2 standard deviations 95% confidence limit) except for natural ratio. 932 Journal of Analytical Atomic Spectrometry November 1995 Vol.10Table 5 Comparison between spiked pure and sea-water calibrations Calibrations from spiked pure water- Parameter s,at 5ngml-I (n=5)(%) Correlation coefficient r Sensitivity/counts ng- mi/i05 Detection limit (3s n= 5)/ng ml-' Calibrations from synthetic sea-water- Parameter s at 5 ng ml-l (n=5) (Yo) Correlation coefficient r Sensitivity/counts ng-l m1/105 Detection limit (3s n = 5)/ng ml-' Mn 1.37 0.9999 9.8 0.53 1.77 0.9971 1.17 11.8 c o 1.75 0.9999 9.0 0.0 1 1.57 0.9985 0.01 10.8 c u 3.19 0.9992 1.9 0.30 1.71 0.9985 2.3 0.38 Zn 3.37 0.9884 2.0 0.38 2.68 0.9898 2.5 0.76 Cd 2.9 1 0.9988 1.2 0.02 2.23 0.9989 0.9 0.05 Table 6 Analysis results for the CRMs SLEW-1 and CASS-2 SLEW-1 CASS-2 Element Mn c o Ni c u Zn Cd Pb ~ Found* 12.7 & 0.4 0.05 1 & 0.003 0.738 _+ 0.049 1.68 k0.03 0.90+0.12 0.01 1 * 0.001 0.026 & 0.002 ~ Certified* 13.1 k0.8 0.046 f 0.007 0.743 _+ 0.078 1.76 & 0.09 0.86 & 0.1 5 0.018 k0.003 0.028 & 0.007 Found* 2.18 rfI 0.19 0.032 & 0.002 0.299 f 0.0 15 0.706 & 0.034 1.95 _+ 0.16 0.01 1 & 0.001 0.019 & 0.006 Certified* 1.99 & 0.15 0.025 & 0.006 0.298 If 0.036 0.675 & 0.039 1.97 & 0.12 0.019 & 0.004 0.019 & 0.006 * Concentrations in ng m1-l.Uncertainties expressed as 2 stand- ard deviations of the instrument response to each analyte (95% confidence limit). and spiked synthetic sea-water matrices as described in Table 5. The two calibration sets compared well therefore validating the use of simple pure water calibration solutions for determining analytes in more complex matrices. This procedure utilized much smaller volumes than would be required using a standard additions procedure and was less susceptible to contamination. The matrix separation procedure was validated by the analysis of the two CRMs SLEW-1 and CASS-2 of similar analyte concentration but different salinity. The analytes were quantified by external calibration against acidified multi- element (Mn Cu Zn Ni Co Cd Pb) pure water standards processed through the manifold.Five repeated analyses were made at each concentration and for the CRMs. The calibrations generally showed good linearity with least-squares regression coefficients of 0.997-0.999 being obtained in the concentra- tion ranges 0-20 ng ml-' (Mn) 0-5 ng ml-' (Cu Ni) and 0-0.1 ng ml - ' (Cd Pb Co). Precisions (measured as relative standard deviation s,) for the selected analytes were in the range 0.9-5.5%. Results for the CRM analyses are given in Table 6. For both materials good agreement between the found and certified values was obtained for all the elements measured.Direct aspiration of the saline CRMs for comparison with the matrix separation procedure was not attempted because of the associated problems of cone and injector blockage and signal suppression in the plasma. Injection of saline samples without prior matrix separation was observed to circumvent blockage problems but significant polyatomic interferences (Table 4) and signal suppression remained. It was considered that these problems coupled with the low analyte concen- trations present in the CRMs rendered direct injection inappropriate for this analysis. CONCLUSIONS A rapid on-line matrix separation procedure using a mini- column of CPG-immobilized 8-HQ was developed.The transient peak signals were successfully monitored using time- resolved data acquisition. A sampling frequency of 15 h-' was obtained with typical measurement precisions of s < 3%. Comparable linear calibrations were obtained from spiked pure and sea-water illustrating that external calibration using pure water solutions was suitable for determining the selected analytes in more complex matrices. Residual matrix retained on the column was shown to not affect the accuracy or precision of the analysis by monitoring the effect of the isobaric interference of 40Ar23Na on Cu in terms of the 63Cu 65Cu ratio. Application of the matrix separation manifold to the estuarine CRM SLEW-1 and the coastal CRM CASS-2 yielded results which were in good agreement with the certified values.These results indicate that ultra-trace element analysis of complex matrix samples is feasible in the absence of clean room facilities. The further application of this manifold to analysis of open-ocean sea-water samples would require a greater degree of preconcentration than is necessary for the coastal and estuarine samples analysed in this study. S.M.N. thanks the EPSRC and Fisons Instruments Elemental Analysis for their provision of funding for this project. REFERENCES 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 Houk R. S. Fassel V. A. Flesch G. D. Svec H. J. Gray A. L. and Taylor C. E. Anal. Chem. 1980,52 2283. Houk R. S. and Olivares J. A. Anal. Chem. 1986 58 20. Shabani M. B. Akagi T. Shimizu H. and Masuda A. Anal. Chem. 1990,62,2709. Sturgeon R. E. Berman S. S. Willie S. N. and Desaulniers J. A. H. Anal. Chem. 1981 53 2337. Olsen S. Pessenda L. C. R. Rbiitka J. and Hansen E. H. Analyst 1983 108 905. Hirata S. Kazuto H. and Kumamaru T. Anal. Chim. Actu 1989 221 65. Bloxham M. J. Hill S. J. and Worsfold P. J. J. Anal. At. Spectrom. 1994 9 935. Malamas F. Bengtsson M. and Johansson G. Anal. Chim. Acta. 1984 160 1. Marshall M. A. and Mottola H. A. Anal. Chem. 1985 57 729. Fang 2.-L. and Welz B. J. Anal. At. Spectrom. 1989 4 543. Beauchemin D. and Berman S. S. Anal. Chem. 1989 61 1857. Fang Z.-L. in Flow Injection Separation and Preconcentration VCH Weinheim 1993 ch. 4. Van Berkel W. W. Overbosch A. W. Feenstra G. and Maessen F. J. M. J. J. Anal. At. Spectrom. 1988 3 249. Habib K. A. J. PhD Thesis University of Hull 1991. Perrin D. D. and Dempsey B. in Bufers for pH and Metal Ion Control ed. Albert A. Chapman and Hall 1974 p. 24. Hill J. M. J. Chromatogr. 1973 76 455. Allen L. A. Pang H. Warren A. R. and Houk R. S. J. Anal. At. Spectrom. 1995 10 267. Paper 5/03072B Received May 15,1995 Accepted July 31 1995 Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 933
ISSN:0267-9477
DOI:10.1039/JA9951000929
出版商:RSC
年代:1995
数据来源: RSC
|
9. |
Computer simulation of enclosed inductively coupled plasma discharges. Part 1. Monatomic gases |
|
Journal of Analytical Atomic Spectrometry,
Volume 10,
Issue 11,
1995,
Page 935-940
Ana Gaillat,
Preview
|
PDF (673KB)
|
|
摘要:
Computer Simulation of Enclosed Inductively Coupled Plasma Discharges Part 1 Monatomic Gases* Journal of Analytical Atomic Spectrometry ANA GAILLAT AND RAMON M. BARNES University of Massachusetts at Amherst Chemistry Department Lederle Graduate Research Tower Box 3451 0 Amherst MA 01 003-451 0 USA PIERRE PROULX AND MAHER I. BOULOS Universitk de Sherbrooke Dkparttment de G6nie Chimique Sherbrooke Qutbec Canada J1 K 2R1 An enclosed inductively coupled plasma (EICP) discharge is simulated with argon and neon and the thermodynamic and fluid flow fields are calculated for a sealed discharge. The influence of discharge container geometry and generator power and frequency are examined. Similarities between the model discharges reflect the thermodynamic and transport properties of argon and neon.Neon model discharges are found to be more stable than their argon counterparts. They exhibit higher maximum temperatures and lower wall temperatures than argon at similar operating frequencies. The velocities in the neon discharge simulation are higher than in an equivalent argon discharge. Keywords Enclosed inductively coupled plasma; computer simulation; argon plasma; neon plasma Optimization of the operation of an enclosed inductively coupled plasma (EICP) is a delicate tedious and expensive process when performed Some of the param- eters that should be considered (container geometry generator frequency and power gas pressure etc.) can be changed within only a very narrow experimental range. This does not always allow exhaustive analysis of potentially ideal operational conditions.The same analysis can be performed theoretically by apply- ing modelling techniques. This approach minimizes experimen- tal time and costs while providing in-depth information about the system. Mathematical modelling of plasma discharges has been applied extensively to the analysis of conventional induc- tively coupled plasmas ( ICP)374 and some enclosed plasma discharges5 With appropriate models the parameters of interest can be varied over a wide range and potentially ideal combi- nations of parameters can be evaluated. For this purpose a simulation model was developed for a sealed EICP in argon and neon.6 Some of the most important parameters that affect the optimum operation of an EICP are generator frequency and power discharge container geometry nature of the discharge gas and gas pressure within the discharge container.The effects of the radiofrequency generator power and frequency and discharge container geometry on EICP argon and neon dis- charges are considered in the present study. These monatomic gases were chosen because of the differences in their transport properties. The temperature and velocity fields within the discharges and the maximum axial and wall temperatures are calculated and compared. EXPERIMENTAL Some of the thermodynamic properties of argon and neon (thermal and electrical conductivities) are illustrated in Fig. 1. Thermal conductivity and specific heat functions are similar for both gases. The main difference between the gases is the considerably lower electrical conductivity of neon than argon corresponding to the higher ionization potential of the f ~ r m e r .~ From the analysis of these properties similar plasma behaviour is expected with the exception that the maximum gas tempera- ture in neon should be higher than in argon. The similarity of the thermal conductivity and specific heat functions of argon and neon indicates that both gases will show similar thermal distributions within the discharge. Since the electrical conduc- tivity of neon is lower and the ionization potential (21.56 eV) is higher than for argon (15.76 eV) the neon discharge will therefore have a tendency to maintain higher temperatures in the plasma than argon. The software employed for these simulations HiFILamp was developed from the HiFI (version 2.2) program described 2.50 2.00 1.50 1 .oo 0.50 0.00 1 .oox1 fl pr- m - .- - g 1.oox10' 6 1.00x100' ' ' ' ' ' ' ' I ' ' ' ' ' ' ' ' ' ' ' " ' ' I ' ' ' 300 2300 4300 6300 8300 10300 12300 14300 TemperaturdK ~~ ~ * Presented at the 1994 Winter Conference on Plasma Spectrochemistry San Diego CA USA January 10-15 1994. Fig.1 Thermodynamic properties as a function of temperature for argon and neon (a) thermal conductivity; and (b) electrical conductivity Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 935by Boulos et aL8 Several modifications have been introduced in the program to account for natural convection radiative transfer effects and the enclosed discharge geometry.6 The model based on steady state laminar flow axial symmetry and local thermodynamic equilibrium (LTE) assumptions provides information about the temperature flow and electro- magnetic fields for spherical and cylindrical container con- figurations with no gas flow (sealed mode).Gaillat et aL6 has described in detail the model and the mathematical algorithm used for the solution of its governing equations. The program allows the variation of multiple operational parameters. The present study explores the effect of generator frequency and power. The container shapes have been restricted to single similar volume cylindrical and spherical geometries. The effect of container size is also not presented in this paper since all possible parameter values fall into one of three categories. For very small containers the simulations are non- convergent or oscillatory. If the container volume is above a critical value the container size has negligible influence on the discharge.For extremely large containers a second critical value is reached above which the convergence is compromised and the results are oscillatory unless extremely high powers are used. The smaller critical value for the container diameter is between 45 and 50mm for most gases. The upper critical dimension is in the range 100-12Omm. These observations agree with experimental evidence since discharges contained in very small containers are unstable and those contained in very large containers require higher powers for their operation.' Another parameter that was not considered in the present study is the plasma gas pressure.Restriction of investigations into this parameter is caused by the lack of tabulated thermo- dynamic and transport properties for the discharge gases over a wide range of pressures. For those parameters that influence the EICP discharge but were not investigated here their numerical values remained unchanged throughout the study. The values assigned to these fixed parameters are as follows. (i) The grid accuracy selected for the simulations was set to 'high thus dividing the discharge volume into 40 control volumes in the axial and 20 in the radial direction.6 (ii) Each simulation was allowed to continue to full convergence regardless of the number of iterations 0 0 0 required. The convergence criterion for the three computational residues of the model was set to less than 1%.(iii) The internal gas pressure in the discharge Container was 101.325 kPa. (iv) The discharge container was assumed to have a 60mm diameter in both spherical and cylindrical conditions. For cylindrical discharges the length of the container also was assumed to be 60 mm. The geometrical layout of the discharge containers has been described previously.6 (v) The induction coil consisted of three turns over a 50 mm length centered on the discharge container in both axial and radial directions. The coil diameter was 66 mm. RESULTS AND DISCUSSION Typical temperature axial and radial velocity field profiles in EICP argon and neon discharges obtained from the simulation are shown in Figs. 2 and 3. As expected from the thermo- dynamic and transport properties of the gases neon produces a higher maximum temperature and a smaller volume simulated discharge than argon.Consequently the discharge container wall temperatures for neon are lower than for argon (cJ Figs. 4 and 5). Similar velocity fields exist in both dis- charges and the smaller neon discharge tends to compact the isocontours. The maximum discharge temperature attainable within a neon EICP model decreases as the generator frequency increases (Fig. 4). This behaviour is due to the delocalization and outward shift of the isotherms resulting from a decrease in the pseudo-skin depth as the generator frequency is increa~ed.~ This effect also causes cooling in the axial region and heating of the container walls. The simulation results obtained for argon (Fig.5) are consistent with those obtained for neon. These trends are expected when literature results for the conventional ICP4 are extrapolated to an enclosed discharge. Comparisons between neon and argon EICP simulations in spherical and cylindrical containers also are shown in Figs. 4 and 5. The model suggests a colder discharge exists in the cylindrical than in the spherical container of the same effective volume. This difference results mainly from the greater possibil- ity for recirculation of the discharge gases in the cylindrical 0 0 0 l c m Fig. 2 A cylindrical EICP argon discharge operated at 40 MHz and 700 W (a) temperature; (b) axial velocity; and (c) radial velocity isocontours. The centre of the induction coil windings is represented by a circle; the central axis of the coil is located on the left side of the plots. The high field is at the upper end of the figures 936 Journal of Analytical Atomic Spectrometry November 1995 Vol.10I I 0 0 F.J I 4- 0 I 0 0 0 0 0 1 cm Fie 3 A cylindrical EICP neon discharge at 40 MHz and 700 W (a) temperature; (b) axial velocity; and (c) radial velocity isocontours. Other - parameters as in Fig. 2 10000 I i 8500 z IJ? g 950 - - g 900 850 800 750 700 650 Spherical Cylindrical I 0 10 20 30 40 50 60 70 80 90 100 FrequencyjMHz Fig.4 Variation with frequency of the maximum temperatures in a neon EICP at 750 W (a) maximum discharge temperature; and (b) maximum wall temperature container.6 The cylindrical discharge container walls also are colder than the spherical container walls.Nonetheless the relative positions of the hottest discharge areas in both geo- metric configurations are comparable. These effects appear more conspicuously for argon than neon. For high powers or frequencies the model argon discharge wall temperatures are increased more than in the neon EICP which in turn decreases the stability of the discharge. Changing the container geometry from a spherical to a cylindrical shape produces a discharge removed from the walls and increases the plasma stability. g500r 9000 g 8500 I- 2 8000 7500 A 1150 1 1 1100 ( b ) 1050 1 1000 Spherical A 950 900 850 800 750 700 10 20 30 40 50 60 70 80 90 100 FrequencyIMHz Fig. 5 Variation with frequency of the maximum temperatures in an argon EICP operated at 750 W (a) maximum discharge temperature; and (b) maximum wall temperature This should extend the practical lifetime of the discharge container.Small systematic changes in the maximum gas velocities in both radial and axial directions occur when the generator frequency is varied in the simulation from 10 to 100 MHz (Figs. 6 and 7). Earlier studies of open ICP discharges demon- strated similar trend^.^ The maximum velocities are related Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 937'. LI -2 t ' I I I I I I I I 0.5 I -3 -0.9 = -1.1 -1.3 1 I I I 1 I I I I 10 20 30 40 50 60 70 80 90 100 Frequencyhl Hz Fig. 6 Variation with frequency of the maximum velocities in a neon EICP operated at 750 W (a) maximum axial velocity; and (b) maximum radial velocity for spherical (A) and cylindrical (+ ) discharge containers 1 I 1 I I I I b 9 -0.3 $ -0.5 E .- E -0.9 - - f -Os7 2 $ 1 -1.1 -1.3 1 ' I 1 I 1 1 I I 10 20 30 40 50 60 70 80 90 100 Freq u ency/M Hz Fig.7 Variation with frequency of the maximum velocities in an argon EICP operated at 750W (a) maximum axial velocity; and (b) maximum radial velocity for spherical (A) and cylindrical (+) discharge containers mainly to the maximum gas temperatures present and not to their position within the plasma. As the frequency of the discharge increases the model suggests the axial and radial velocity field isocontours are displaced as is the temperature field towards the container walls.The small asymmetries in the axial velocity fields shown in Fig. 8 Variation with power of the maximum temperatures in a neon EICP operated at 40 MHz (a) maximum discharge temperature; and (b) maximum wall temperature I 9700 9200 5 hE 8700 8200 7700 950 1 Cylindrical 00 1000 1100 1200 1300 1400 1500 PowerMl Fig.9 Variation with power of the maximum temperatures in an argon EICP operated at 40 MHz (a) maximum discharge temperature; and (b) maximum wall temperature 938 Journal of Analytical Atomic Spectrometry November 1995 Vol.102 I -2 h 1.5 r u) \ € 1 x c. .- 8 0.5 - 9) G o .- .- i -0.5 x -l -1.5 1 I I I I I I 1 I 0.5 I 1 L -2 - I 1 I I I I I 1 I 500 600 700 800 900 1000 1100 1200 1300 1400 1500 PowerNV 500 600 700 800 900 1000 1100 1200 1300 1400 1500 PowerNV Fig. 10 Variation with power of the maximum velocities obtained in a neon EICP operated at 40MHz (a) maximum axial velocity; and (b) maximum radial velocity for spherical (A) and cylindrical (+) discharge containers Figs.6 and 7 are due to the presence of small secondary recirculation areas. The noticeable asymmetry in the radial velocity can be explained by considering the field geometry (Fig. 3). The radial velocity field simulation exhibits only one negative velocity region but it presents two nearly equivalent areas of positive velocities. Therefore to keep the recirculation balance the absolute value of the negative velocities has to be approximately twice that of the positive components. The effects of increasing power in the argon and neon model EICP discharges are illustrated in Figs. 8 and 9. As more power is available to the discharge all the discharge tempera- ture fields increase.This is also anticipated from corresponding experience with open ICPS.~ A marked increase in gas velocities follows the increase in generator power because more kinetic energy is made available to the gas at higher radiofrequency powers. The results shown in Figs. 10 and 11 demonstrate parallel trends for argon and neon EICPs. Differences in the absolute values of the fields exist for the two EICP geometric configurations. However the maximum temperatures in neon are influenced less by the container shape than in argon (Figs. 8 and 9). Both gases show a completely analogous behaviour for both container geometries. In all cases the discharges are symmetrical alongside the main axis (ie. the induction coil axis) with only a very small (less than 10%) extension of the discharge towards the high field areas.The simulated effects of frequency and power on a neon discharge are analogous to those for argon even though the gases possess different thermodynamic and transport proper- ties. Therefore argon and neon could be used interchangeably as EICP discharge gases. However the optimum operating conditions for both gases will differ. For all power and fre- quency conditions examined the model suggests that neon Fig. 11 Variation with power of the maximum velocities obtained in an argon EICP operated at 40 MHz (a) maximum axial velocity; and (b) maximum radial velocity for spherical (A) and cylindrical (+) discharge containers produces a hotter and smaller discharge than argon. The wall temperatures generally are lower partly owing to the relatively smaller size of the neon discharge.Within the commonly used ICP operating frequency range (10-100 MHz) the model suggests that both gases behave consistently. No unique frequency exists from the point of view of performance or stability. Neon can be operated at lower frequencies than argon without detriment to the spectroscopic characteristics of the discharge owing to its higher thermo- dynamic temperatures. Thus to produce a required maximum discharge temperature value the model suggests that the operating power necessary for a neon discharge will be lower than for argon. Some of the critical features to consider for a potential discharge support gas are optimum excitation temperature freedom from spectral interferences and conservative use of the discharge container. Typically a compromise among sev- eral of these parameters is needed.If a higher excitation temperature is required the model suggests that changing the discharge gas from argon to neon could be adequate to produce a suitable analytical environment under the frequency and power conditions for which argon would produce a discharge with insufficient thermal energy. Substitution of neon for argon can result in an increase in maximum discharge and axial temperatures without an increase in the wall tempera- tures. The simulated temperature gradients present in both axial and radial directions are more pronounced in neon than in argon resulting in a concentrated discharge removed from the walls of the container.This effect nevertheless does not produce an extreme reduction in the size of the plasma which would make imaging of the analysing optics difficult. Because the wall temperatures in a cylindrically contained discharge remain considerably colder than in an equivalent spherical Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 939container employing a cylindrical instead of a spherical dis- charge container should extend the lifetime of the container without sacrificing spectroscopic performance. Practical EICP discharges in neon krypton and xenon at 350-400 W in a 65,mm spherical container have been generated experimentally to observe their atomic emission spectra from 200 to 900nm.lo Extending the EICP simulation to krypton and xenon requires only the substitution of the appropriate thermodynamic and transport properties.Since these two gases resemble argon in all their thermodynamic and transport properties the results obtained in the simulation of krypton and xenon EICP discharges are fully analogous with those of an argon plasma. Analyte excitation in argon and neon EICP discharges has not been considered in the present investigation although differences in excitation processes described for argon and neon in a radiofrequency boosted pulsed hollow cathode lamp,ll for example can be expected in an EICP. Excited-state populations of atoms and ions in argon and helium12 ICP discharges deviate from LTE. A neon discharge is expected to exhibit non-LTE characteristics between argon and helium since the mass and ionization potential of neon are between those of helium and argon.The model needs to be extended to incorporate non-LTE conditions to describe the argon and neon EICP discharges fully. This research was sponsored by the ICP Information Newsletter. REFERENCES 1 2 3 4 5 6 7 8 9 10 11 12 Jahl M. J. Jacksier T. and Barnes R. M. J. Anal. At. Spectrorn. 1992 7 653. Jacksier T. and Barnes R. M. J. Anal. At. Spectrom. 1992,7,839. Barnes R. M. and Yang P. Y. Spectrochim. Acta Rev. 1990 13 275. Boulos M. I. and Barnes R. M. in Inductively Coupled Plasma Emission Spectroscopy Part I I ed. Boumans P. W. J. M. John Wiley New York 1987 ch. 9. Paik S. H. and Pfender E. Plasma Chem. Plasma Proc. 1990 10 167. Gaillat A. Barnes R. M. Proulx R. and Boulos M. I. Spectrochim. Acta Part B in the press. Dresvin S . V. Physics and Technology of Low Temperature Plasmas Iowa State University Press IA 1977. Boulos M. I. Mostaghimi J. and Proulx P. High Frequency Induction Plasma UniversitC de Sherbrooke Sherbrooke 1989. Boulos M. I. Pure Appl. Chem. 1985 57 1321. Jacksier T. and Barnes R. M. Appl. Spectrosc. 1994 48 65. Farnsworth P. B. and Walters J. P. Spectrochim. Acta Part B 1982 37 773. Cai M. Montaser A. and Mostaghimi J. Spectrochim. Acta Part B 1993 48 789. Paper 5/02348C Received April 11 1995 Accepted July 17 1995 940 Journal of Analytical Atomic Spectrometry November 1995 Val. 10
ISSN:0267-9477
DOI:10.1039/JA9951000935
出版商:RSC
年代:1995
数据来源: RSC
|
10. |
Computer simulation of enclosed inductively coupled plasma discharges. Part 2. Molecular gases |
|
Journal of Analytical Atomic Spectrometry,
Volume 10,
Issue 11,
1995,
Page 941-946
Ana Gaillat,
Preview
|
PDF (722KB)
|
|
摘要:
Computer Simulation of Enclosed Inductively Coupled Plasma Discharges Part 2*. Molecular Gasest Journal of Analytical Atomic Spectrometry ANA GAILLAT AND RAMON M. BARNES University of Massachusetts at Amherst Chemistry Department Lederle Graduate Research Tower Box 34510 Amherst MA 01 003-4510 USA PIERRE PROULX AND MAHER I. BOULOS Universitk de Sherbrooke D6partkment de Gknie Chimique Sherbrooke Qukbec Canada J1 K 2R1 The thermodynamic and fluid flow fields within hydrogen nitrogen and oxygen enclosed inductively coupled plasma (EICP) discharges are calculated using a novel computer simulation. Nitrogen and oxygen discharges give easily convergent results and are more stable than a hydrogen discharge calculation. The maximum calculated plasma temperatures in 700 W 40 MHz EICP discharges are 10 500 K for hydrogen 10 200 K for oxygen 8300 K for argon and 6500 K for nitrogen.The corresponding maximum axial velocities are 48 m s-' for hydrogen 9.2 m S-' for oxygen 1.2 m s-l for argon and 0.36 m s-' for nitrogen. The hydrogen discharge simulation exhibits higher temperature and velocity gradients than oxygen argon or nitrogen. Keywords Enclosed inductively coupled plasma; computer simulation; hydrogen plasma; nitrogen plasma; oxygen plasma 16.0 14.0 L 12.0 7 10.0 .t > 8.0 .- c 3 6.0 F E FE - (D 4.0 0 2.0 0.0 300 2300 4300 6300 8300 10300 12300 14300 Temperature/K The development of a practical enclosed inductively coupled plasma (EICP) discharge enables the formation and appli- cation of atmospheric pressure discharges with gases typically not employed for conventional inductively coupled plasma (ICP) sources. For example the atomic spectra of chlorine,' neon krypton and xenon2 from EICP discharges have been reported recently.Optimization of these laboratory discharges can be aided by computer simulations and a comparison of argon and neon EICP simulation was illustrated in Part 1 of this ~eries.~ In the present paper the EICP computer simulation has been extended to molecular gases including hydrogen nitrogen and oxygen. Diatomic gas transport and thermo- dynamic properties differ significantly from those of monatomic gases principally because of the dissociation of the molecule into atoms. Consequently the computer simulation requires modification to accommodate the calculations relevant to molecular gases.Computer models of conventional ICP discharges have included heli~m,~ argon nitrogen and oxygen,' but reports on a hydrogen ICP simulation are scarce.6 No experimental hydrogen ICP spectrochemical discharge has been described. In one comparison the maximum calculated temperatures were 10400 K for argon 8950 K for oxygen 7510 K for nitrogen and 6830 K for hydrogen.6 Hydrogen oxygen and most diatomic molecules dissociate at fairly low temperatures compared with nitrogen and their thermodynamic and transport properties differ significantly. Dissociation of hydrogen and oxygen causes a maximum in their thermal conductivity and heat capacity at 3000-4000 K (Figs. 1 and 2). The maximum for nitrogen is about 7000 K. Consequently hydrogen and oxygen behave fairly differently to nitrogen or monatomic gases in plasma discharges and the * For Part 1 of this series see ref.3. t Presented at the 1994 Winter Conference on Plasma Spectrochemistry San Diego CA USA January 10-15 1994. Fig. 1 Thermal conductivity as a function of temperature for argon hydrogen nitrogen and oxygen 2 % 1 . 0 ~ 1 0 ~ .= 2 . 0 ~ 1 0 ~ 300 2300 4300 6300 8300 10300 12300 14300 I I / 0 6.0~10~ g 8.0~10~ ? 4 . 0 ~ 1 0 ~ o.ox1oo Temperature/K Fig. 2 Heat capacity as a function of temperature for argon hydrogen nitrogen and oxygen size of the discharge should be small and the maximum temperature high. However the electrical conductivities of argon and oxygen are higher below 7000K than those of hydrogen and nitrogen. In earlier simulations substantial differences were found in Joule heating and temperature fields for hydrogen and oxygen ICP discharges although their dissociation behaviour is similar.6 The goal of the present investigation is to examine the properties of these molec- ular gas discharges by computer simulation of the EICP configuration.EXPERIMENTAL The EICP model and its mathematical algorithm used for the solution of the governing equations have been described by Journal of Analytical Atomic Spectrometry November 1995 Vol. 10 941Gaillat et ~ 1 . ~ The model is based on steady state laminar flow axial symmetry and local thermodynamic equilibrium assumptions (LTE) and provides information about the tem- perature flow and electromagnetic fields for spherical and cylindrical discharge configurations in the sealed (no flow) mode.The program HiFILamp also includes natural convec- tion and radiative transfer effects as well as the enclosed characteristics of the discharges. The version of HiFILamp used for these simulations consists of the option of extra high density grids. In this configuration the total control volume is divided into 40 x 80 cells. The modelling of EICP diatomic gas discharges presents some practical problems which arise from the same properties that make these plasmas useful. For hydrogen and oxygen discharges the characteristic sharp plasma temperature gradi- ents require use of extra high density grids (40x80) for the computer ~imulation.~ With only high density grids (40 x 20) non-convergent or unstable results are obtained.* For mon- atomic gases (argon helium neon etc.) and high dissociation temperature diatomic gases such as nitrogen the use of extra high density grids (40 x 80) in the computer simulation does not provide sufficient advantage to outweigh the increased processing time required.When hydrogen and oxygen enclosed plasmas are simulated with extra high density calculation grids (40 x 80) convergent and stable solutions are obtained for a wide range of power and frequency operating conditions for cylindrical and spheri- cal geometric configurations. However only one set of results is presented here for a 60 mm spherical container at 700 W and 40 MHz. Of all the operating parameters that can be studied with this program only the gas properties are changed in this investigation.The values of the geometrical parameters are kept constant and all fixed parameters values assigned have been described in Part l.3 The processing time for a fully convergent simulation when using extra high density grids for hydrogen and oxygen is approximately 2 h with a Dell 486/33 MHz personal computer. Under similar convergence requirements a standard high density simulation for argon and nitrogen takes approximately 1 h with the same computer. RESULTS AND DISCUSSION One objective of the present study was to establish accurate and stable simulation results for hydrogen and oxygen EICP discharges. Molecular gases exhibit maxima in their thermal conductivity and heat capacity as a function of temperature at their dissociation temperature^^,'^ as shown in Figs.1 and 2. This characteristic defines the behaviour of a discharge by controlling the shape and size of the highest temperature areas within the discharges.' Thermal conductivity and specific heat functions for hydro- gen nitrogen and oxygen are similar. The feature that domi- nates each of these curves is the peak in the distribution of these properties with respect to temperature resulting from the dissociation of the gases. The main difference amongst these three gases consists of the location of the dissociation maxima. While hydrogen and oxygen properties peak at temperatures well below the operating temperature of an EICP nitrogen shows a maximum at much higher temperatures. From the analysis of the properties of these gases similar behaviour is expected for hydrogen and oxygen which will differ markedly from those of nitrogen or argon.Argon hydrogen nitrogen and oxygen EICP spherical dis- charges generated with the same generator power (700 W) and frequency (40 MHz) are compared in Fig. 3. The 6000 K iso- therm for the four discharges represents their different shapes and sizes. The model suggests that hydrogen produces the (2 f ) 0 0 0 Fig. 3 Position and shape of the 6000 K isotherm for argon hydrogen nitrogen and oxygen EICP discharges operated at 40 MHz and 700 W in a spherical container. Results obtained by using the values of the fixed parameters presented in ref. 3. The centre of the induction coil windings are represented by the circles most compact discharge followed by oxygen nitrogen and argon.In contrast to the results of Yu and Girshick,' the hydrogen and oxygen discharges are hottest (10490 and 10 170 K respectively) followed by argon (8320 K) and nitro- gen (6460 K). The high temperatures and the shape of the hydrogen and oxygen plasmas are potentially useful as ETCP support gases. The small discharge size will keep the container walls relatively cool and increase the lifetime of the containers. The temperature axial and radial velocity fields for hydro- gen oxygen nitrogen and argon EICPs at 700 W and 40 MHz are illustrated in Figs. 4-7 respectively. The radial and axial temperatures at different locations in the induction coil are plotted in Figs. 8-13. The differences in the thermodynamic properties of the gases are responsible for the diversity in the temperature and velocity fields for these EICP discharges. These properties characterize the discharge by controlling the shape and size of the highest temperature areas (Fig.3). These observations are supported by a systematic study of the influence of these properties on the discharge fields which has been presented recently.'' The plasmas produced with hydrogen and oxygen in the simulation are hotter and more compact than those calculated for nitrogen and argon. This effect is apparent in both axial and radial directions (Figs. 8 and 9). Although the dissociation energies for hydrogen nitrogen and oxygen are high (435.72 948.93 and 497.48 kJ mol-l respectively) the temperature at which the dissociation occurs controls the properties of the discharge. The temperatures at which hydrogen nitrogen and oxygen reach 50% dissociation are 4285 7075 and 3759K respectively.Hydrogen and oxygen produce discharges that are cooler in the periphery where the dissociation processes principally occur. In the central regions of the plasma where most of the gas molecules are already dissociated the tempera- tures reached by the hydrogen and oxygen discharges are considerably higher than in an argon or nitrogen EICP. These two effects result in a model discharge with a very hot and highly localized core and a cooler outside area (Figs. 10 and 11). The hydrogen discharge is smaller and hotter because its transport properties (e.g. heat capacity) are higher than those 942 Journal of Analytical Atomic Spectrometry November 1995 Vol.100 0 Fig.4 A cylindrical EICP hydrogen discharge operated at 40MHz and 700 W (a) temperature; (b) axial velocity; and (c) radial velocity isocontours 3 3 0 0 0 0 0 0 Fig. 5 A cylindrical EICP oxygen discharge operated at 40 MHz and 700 W (a) temperature; (b) axial velocity; and (c) radial velocity isocontours of oxygen. These predictions are significantly different from the conclusions reached by Yu and Girshick,' who calculated much cooler hydrogen than oxygen discharges. The simulated oxygen EICP results are however consistent with earlier models of and experimental data for conventional oxygen ICP discharge^.^,^^ For the nitrogen EICP isotherms throughout the simulated discharge are more homogeneously distributed than in the other diatomic gases (Fig.12) because the maximum discharge temperature is lower than the maximum of the nitrogen dissociation temperature. Although nitrogen dissociation requires more energy at high temperatures than hydrogen and oxygen the nitrogen discharge maintains a uniform radial temperature as does the argon EICP. These results also parallel earlier models of conventional nitrogen ICP discharges.13 Since argon is monatomic the discharge produced extends uniformly almost to the container wall (Fig. 13). The homo- geneous temperature distribution calculated for the EICP is very similar to that observed for a conventional argon ICP without a central flow.14 Axial and radial velocity fields increase as the computed plasma isotherms shrink and the maximum discharge tempera- ture increases.Almost a factor of five distinguishes the maxi- mum axial flow rates between the gases. The maximum axial velocities are 47.7 m s-l for hydrogen 9.22 m s-l for oxygen 1.17 m s-' for argon and 0.36 m s-' for nitrogen. Radial velocities also increase in the same order. Very fast gas flow in the hydrogen discharge is predicted with high radial flow into the side of the discharge in the centre of the induction coil. This high axial and radial velocity rather than the small hot discharge could be the limiting characteristic that prevents the easy generation of a practical hydrogen ICP discharge. The response of the model discharge to changes in the generator power and frequency is shown in Figs. 14 and 15 respectively. The effects of increasing power in all the EICP discharges studied are as expected.As more energy is available to the discharge all the discharge temperature fields increase. This is also anticipated from corresponding experience with open ICPs.' In addition the temperature field isocontours are displaced towards the container walls with the increase of the Journal of Analytical Atomic Spectrometry November 1995 VoZ. 10 943. . 0 0 0 3 3 0 -0.05 2 0.15 0 Fig.6 A cylindrical EICP nitrogen discharge operated at 40 MHz and 700W (a) temperature; (b) axial velocity; and (c) radial velocity isocontours pj -0.6 3 3 0 0 0 c -0.2 - ‘0 - /I Fig. 7 A cylindrical EICP argon discharge operated at 40 MHz and 700 W (a) temperature; (b) axial velocity; and (c) radial velocity isocontours 12000 l2O0O - 10000 0 -f C .i 8000 g 6000 - a 3 4000 I- 3 2000 10000 8000 s 8j CI 2 6000 .- - c.5 4000 0 2000 t I I I I 5 I 10 15 20 25 30 rlrnm Fig.8 Radial temperature profile at axial grid point 40 (middle of the coil) for argon hydrogen nitrogen and oxygen cylindrical EICP discharges operated at 40 MHz and 700 W I I I I I L I 20 30 40 50 60 10 z /mm Fig. 9 Axial temperature profile at the coil axis; for argon hydrogen nitrogen and oxygen cylindrical EICP dischargeis operated at 40 MHz and 700 W 944 Journal of Analytical Atomic Spectrometry November 1995 Vol. 10l2OO0 9 % 5000 t- 4000 3000 2000 1000 Grid int 60 400: 2000 r /rnm Fig. 10 Radial temperature profiles of a 40 MHz and 700 W hydrogen cylindrical EICP discharge at grid point 20 (beginning of the coil) grid point 40 (middle of the coil) and grid point 60 (end of the coil) - 1 12000 1 10000 8000 % 6000 L 4000 2000 I I I I I 5 10 15 20 25 30 rlmm Fig.11 Radial temperature profiles of a 40 MHz and 700 W oxygen cylindrical EICP discharge at grid point 20 (beginning of the coil) grid point 40 (middle of the coil) and grid point 60 (end of the coil) 7000 Grid-point 40 6000 5000 5 4000 3000 2000 1000 I 5 10 15 20 25 30 rlrnrn Fig. 12 Radial temperature profiles of a 40 MHz and 700 W nitrogen cylindrical EICP discharge at grid point 20 (beginning of the coil) grid point 40 (middle of the coil) and grid point 60 (end of the coil) generator frequency in good agreement with literature and experimental data. Within the commonly used ICP operating frequency range (10-100 MHz) the model suggests that all the gases behave consistently. No unique frequency exists from the point of view of performance or stability. If the spectroanalytical application requires a high- temperature high-velocity plasma the model suggests that hydrogen and oxygen are the preferred gases. This conclusion corresponds to earlier observations for conventional ICP dis- charge~.~~'~ A plasma supported by either hydrogen or oxygen 7000 6000 1 Gridmid60 \ ' \\ I 0 I I I I I 5 10 15 20 25 30 I r /mrn Fig.13 Radial temperature profiles of a 40 MHz and 700 W argon cylindrical EICP discharge at grid point 20 (beginning of the coil) grid point 40 (middle of the coil) and grid point 60 (end of the coil) 12900 11900 10900 y 9900 8900 7900 6900 5900 1350 r 750 500 700 900 1100 1300 1500 1700 1900 PoweriW Fig.14 Effect of generator power on (a) the maximum discharge temperature and (b) the maximum wall temperature for argon hydro- gen nitrogen and oxygen cylindrical EICP discharges operated at 40 MHz will displace the hot discharge from the container walls minimize thermal failure and improve the operating lifetime of the container.l69l7 However hydrogen can diffuse through hot quartz walls in practical EICP discharges containing hydrogen and the discharge lifetime in a sealed EICP is finite." Thus an oxygen EICP could be easier to operate for extended periods.Nitrogen and argon EICP simulations predicted homo- geneous axial and radial temperature distributions. The dis- charges closely approach the container walls potentially jeopardizing the integrity of the quartz.13 These results agree with qualitative experimental data available for EICP discharges.Molecular gas EICP simulations provide data for nitrogen and oxygen discharges consistent with conventional ICP discharge experimental and computed results. Molecular gases produce discharges smaller than those supported by argon Journal of Analytical Atomic Spectrometry November 1995 VoZ. 10 94512000 (a 11 11000 10000 y 9000 t-!! 8000 7000 1 N I z E ' I I ~ 1 ' 600 10 20 30 40 50 60 70 80 90 100 FrequencyIMHz Fig. 15 Effect of generator frequency on (a) the maximum discharge temperature and (b) the maximum wall temperature for argon hydro- gen nitrogen and oxygen cylindrical EICP discharges operated at 700 w with the oxygen plasma supporting higher temperatures than both argon and nitr~gen.~ New results have been computed for hydrogen that appear self-consistent with its properties and other molecular gases.An extra high density grid is necessary and effective for hydrogen and oxygen calculations. The results of this model for argon nitrogen and oxygen correspond closely to earlier results from models and experimental measurements for conventional ICP discharges. The predicted hydrogen EICP discharge is therefore also expected to rep- resent accurately the hydrogen ICP discharge. Verification however requires that a practical hydrogen ICP be produced experimentally. Furthermore the direct application of the EICP simulation to other diatomic gases (e.g. chlorine and hydrogen chloride) is expected.The effects of frequency and power on model hydrogen nitrogen and oxygen discharges are analogous with those for argon although the gases possess different thermodynamic and transport properties. For all power and frequency conditions examined hydrogen produces the hottest and smallest simu- lated discharge followed by oxygen argon and nitrogen. The wall temperatures in a model hydrogen discharge generally are lower owing to the relatively smaller size of the discharge. This effect is less pronounced with oxygen although the simulated wall temperatures are still considerably lower than those present in an argon plasma. An important practical limitation to the application of an argon EICP even at relatively low generator power is the relatively high wall temperatures which can reach the softening point of quartz.Therefore unless the discharge is sustained at very low frequen- cies the operating range for the power of an argon plasma will be considerably smaller than that of a molecular gas. In contrast the simulated hydrogen EICP model results agree with the experimental observation that with the addition of hydrogen to an EICP discharge the discharge is reduced and moved away from the container walls. Thus in hydrogen admixtures the lifetime of practical EICP containers is extended. This research was sponsored by the ICP InJorrnation Newsletter. REFERENCES 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 Jacksier T. and Barnes R. M. Appl. Spectrosc. 1994 48 65. Jacksier T. and Barnes R. M. Appl. Spectrosc.1994 48 385. Gaillat A. Barnes R. M. Proulx P. and Boulos M. I. J. Anal. At. Spectrom. 1995 10 935. Cai M. Montaser A. and Mostaghimi J. Spectrochim. Acta Part B 1993 48 789. Barnes R. M. and Yang P. Y. Spectrochim. Acta Rev. 1990 13 275. Yu W. and Girshick S. L. Proceedings cf the 9th International Symposium on Plasma Chemistry Pugnochiuso Italy September Gaillat A. Barnes R. M. Proulx P. and Boulos M. I. Spectrochim. Acta Part B in the press. Boulos M. I. Mostaghimi J. and Proulx P. High Frequency Induction Plasma UniversitC de Sherbrooke Sherbrooke 1989. Dresvin S . V. Physics and Technology of Low Temperature Plasmas Iowa State University Press IA 1977. Kurtz A. and Mentel J. J. Phys. D Appl. Phys. 1984 17 1343. Gaillat A. M. and Barnes R. M. paper presented at the 1995 European Winter Conference on Plasma Spectrochemistry Cambridge UK January 1995 paper M1. Yang P. and Barnes R. M. Spectrochiwr. Acta Part B 1989 44 1093. Barnes R. M. Kovacic N. and Meyer G. A. Spectrochim. h a Part B 1985 40 907. Barnes R. M. and Schleicher R. G. Spectrochim. Acta Part B 1985 40 81. Boulos M. I. and Barnes R. M. in Inductively Coupled Plasma Emission Spectroscopy Part 11 ed. Boumans P. W. J. M. John Wiley New York 1987 ch. 9. Jacksier T. and Barnes R. M. J. Anal. At. Spectrom. 1992,7,839. Jahl M. J. Jacksier T. and Barnes R. M. J. Anal. At. Spectrom. 1992 7 653. Jacksier T. and Barnes R. M. J Anal. At. Spectrom. 1994,9,1299. 1989 V O ~ . 1 pp. 31-36. NOTE-Ref. 3 is to Part 1 of this series. Paper 5 J02349A Received April 11 1995 Accepted July 17 1995 946 Journal of Analytical Atomic Spectrometry November 1995 Vol. 10
ISSN:0267-9477
DOI:10.1039/JA9951000941
出版商:RSC
年代:1995
数据来源: RSC
|
|