Methyl-hydrazine deoxidize Tc(VII) in nitric acid in presence of U(VI) and behavior of technetium in the U/Pu splitting stage of APOR process

Similar documents
Chemical Separations of Pu- 238 from Irradiated Neptunium Targets

Solvent Extraction 9-1

Separation process modelling. B. Dinh, M. Montuir, C. Sorel, X. Héres. Département de RadioChimie et Procédés CEA 10 AVRIL 2012 PAGE 1

SOME ELEMENTS AND ISOTOPES OF SPECIAL CONCERN IN FUEL CYCLE C SEPARATIONS S Tc: ( 99 Tc) U: ( 3 U, 33 U, 34 U, Np: ( 37 Np) Pu: ( 38 Pu, 39 Pu, Am: (

PRODUCTION OF URANOUS NITRATE WITH HYDRAZINE NITRATE AS REDUCING AGENT IN PRESENCE OF ADAMS CATALYST FOR URANIUM RECONVERSION PURPOSES

Studies in liquid-liquid systems. the components of a solution by distributing them between two liquid phases. Its applications

Available online at ScienceDirect. Energy Procedia 89 (2016 )

Science and Technology. Solutions, Separation Techniques, and the PUREX Process for Reprocessing Nuclear Waste

Nitrogen Oxide Closed System

Application of Phosphorus-Containing Ion Exchangers for the Recovery and Separation of Uranium and Transuranic Elements

Uranium (IV)-(VI) Electron Exchange Reactions in

Chapter 13. Solution Dynamics

Available online at Indian Journal of Advances in Chemical Science 3(2) (2015)

THE THERMAL OXIDE REPROCESSING PLANT AT SELLAFIELD: Four Years of Successful Treatment of Irradiated Nuclear Fuel

Cycle Separations. Terry Todd. CRESP Short Course -Introduction to Nuclear Fuel Cycle Chemistry Crystal City, VA

Not Reviewed by WMSymposia, Inc. Purex Process Improvements for PU and NP Control in Total Actinide Recycle Flowsheets

Complexation Reactions In Nuclear Separations. Raymond G. Wymer Vanderbilt University

Continuous Extraction and Stripping of Neptunium By Fresh and Degradated Tributyle Phosphate Using Co-60 Cell

Rapid Separations. Activity Radioactive Solutions. Lawrence Jassin Eichrom Technologies LLC March 3, 2008 Pittcon 2008

SEPARATION OF MINOR ACTINIDES FROM A GENUINE MA/LN FRACTION. Abstract

Available online at ScienceDirect. Procedia Environmental Sciences 31 (2016 )

Neptunium behaviour in PUREX and GANEX processes

Application Note. Abstract. Introduction. Experimental

Cation-exchange separation of uranium from thorium in nitric acid medium

RECENT PROGRESSES ON PARTITIONING STUDY IN TSINGHUA UNIVERSITY

SVENSK STANDARD SS-ISO :2007

Technical note. Risks of explosion associated with "red oils" in reprocessing plants

THORIUM, PLUTONIUM, AND URANIUM IN WATER

STUDY ON PARTITIONING OF LONG LIVED NUCLIDES FROM HLLW IN TSINGHUA UNIVERSITY

XA IAEA-TECDOC-1051

Available online at ScienceDirect. Procedia Environmental Sciences 31 (2016 )

EXTRACTION OF URANIUM (VI) FROM NITRIC ACID AND NITRATE SOLUTIONS BY TRIBUTYLPHOSPHATE/KEROSENE

Study on kinetics of adsorption of humic acid modified by ferric chloride on U(VI)

WM2014 Conference, March 2 6, 2014, Phoenix, Arizona, USA

Characterization of High Level Liquid Waste Generated from Reprocessing of Power Reactor Spent Fuel

Solvent Extraction Research and Development, Japan, Vol. 22, No 1, (2015)

Redox Chemistry of Neptunium in Solutions of Nitric Acid

Reprocessing of spent mixed nitride U-Pu fuel from BREST-OD-300 reactor ShadrinA.Yu., Dvoeglazov K.N., Ivanov V.B.

CHEM 312: Lecture 13 Neptunium Chemistry

Mass transfer kinetics of uranium(vi) and plutonium(iv) extracted by N,Ndialkylamides. Comparison of different techniques

Matrix and High Loading Effects on Eichrom Resins. Dan McAlister and Phil Horwitz Eichrom Workshop October 31, 2012

Removal of Uranium from Plutonium Solutions by Anion Exchange

Contact Person(s) : Anna Berne APPLICATION

Study on Electrochemical Properties of Palladium in Nitric Acid Medium

enable measurement. This method separates these isotopes effectively.

Stir Bar Sorptive Extraction modelling for hydrometallurgical extracting molecules, and LC-MS analytical method for environmental applications

Trioctylphosphine Oxide. Citation University (1975), 52(5-6):

CHAPTER - 2 EXPERIMENTAL TECHNIQUE. Potassium permanganate has been used for. oxidation of many systems. Oxidations by permanganate

ELECTROCHEMICAL METHODS FOR REPROCESSING DEFECTIVE FUEL ELEMENTS AND FOR DECONTAMINATING EQUIPMENT. S.V.Mikheykin, K.A.Rybakov, V.P.

Sodium Chloride - Analytical Standard

WM2012 Conference, February 26 March 1, 2012, Phoenix, Arizona, USA

Recent Activities on R&D of Innovative Extractants and Adsorbents for Partitioning of Minor Actinides at JAEA

Westinghouse Nuclear Company, Idaho Inc.

Actinides (f-block) 1-1

Infl uence of alpha and gamma radiolysis on Pu retention in the solvent TBP/kerosene

Plutonium Third Phase Formation in the 30% TBP/Nitric Acid/Hydrogenated Polypropylene Tetramer System

CONCEPTUAL DESIGN FOR SEPARATION OF PLUTONIUM AND GALLIUM BY SOLVENT EXTRACTION

MOF-76: From Luminescent Probe to Highly Efficient U VI Sorption Material

Extraction of uranium from acidic media with a novel synergistic mixture of di-nonyl phenyl phosphoric acid and tri-n-octyl phosphine oxide

Robust Speed Controller Design for Permanent Magnet Synchronous Motor Drives Based on Sliding Mode Control

EXPERIENCE OF TEST OPERATION FOR REMOVAL OF FISSION PRODUCT NUCLIDES IN TRU-LIQUID WASTE AND CONCENTRATED NITRIC ACID USING INORGANIC ION EXCHANGERS

MANAGEMENT OF SPENT SOLVENTS OF REPROCESSING ORIGIN

URANIUM IN SOIL. Analytical Procedure (2 GRAM SAMPLE) 1. SCOPE

Modifying U/Pu separation chemistry in Purex processes Robin Taylor. Date: 02/12/09

TECHNETIUM-99 IN SOIL

Production. David Nusbaum Project on Managing the Atom, Belfer Center October 4, 2011

Solution-processable graphene nanomeshes with controlled

Chem II - Wed, 9/14/16

Removal of Carbon Dioxide from Indoor Air Using a Cross- Flow Rotating Packed Bed

#89 Notes Unit 11: Acids & Bases and Radiochemistry Ch. Acids, Bases, and Radioactivity

--> Buy True-PDF --> Auto-delivered in 0~10 minutes. GB Translated English of Chinese Standard: GB5009.

Complexation Chemistry and

Spectroscopic Online Monitoring for Process Control and Safeguarding of Radiochemical Fuel Reprocessing Streams 13553

CH0204 Organic Chemical Technology

Determination of plutonium isotopes in spent nuclear fuel using thermal ionization mass spectrometry (TI-MS) and alpha spectrometry

Available online at ScienceDirect. Energy Procedia 63 (2014 ) GHGT USA

Radiochemistry in reactor

Radiochemistry Webinars

Separation of An(III) from PUREX raffinate as an innovative SANEX process based on a mixture of TODGA/TBP

Patricia Paviet-Hartmann Los Alamos National Laboratory, Carlsbad Operations Environmental Science and Waste Technology Division Carlsbad, NM 88220

TECHNETIUM-99 IN WATER

AP Chemistry Unit 2 Test (Chapters 3 and 4)

SEPARATION OF MINOR ACTINIDES FROM GENUINE HLLW USING THE DIAMEX PROCESS

AP Chemistry Review Packet #1

ScienceDirect. Impact of heat stable salts on equilibrium CO 2 absorption

Chapter 37. Nuclear Chemistry. Copyright (c) 2011 by Michael A. Janusa, PhD. All rights reserved.

Relationship between the characteristics of cationic polyacrylamide and sewage sludge dewatering performance in a full-scale plant

PREPARATION OF URANIUM (IV) NITRATE SOLUTIONS. by R. S. Ondrejcin. July 1961

Form 4 Chapter 7: Acid and Bases

Nuclear Fuel Reprocessing. By Daniel Bolgren Jeff Menees

LACTIC ACID. The method is applicable to the determination of lactic acid and lactate salts (Note 2) in light or heavy steepwater.

Unit 4: Chemical Changes (Higher Content)

Sequential Determination of Free Acidity and Plutonium Concentration in the Dissolver Solution of Fast-Breeder Reactor Spent Fuels in a Single Aliquot

VI. 1. Development of a Simplified MA Separation Process Using Novel R-BTP Adsorbents II

WM2012 Conference, February 26 March 1, 2012, Phoenix, AZ

RADIOLOGICAL CHARACTERIZATION Laboratory Procedures

Measurements: Radiochemical separation methods and radiometric analysis. Equipment and radionuclides.

Research and Development to Reduce Radioactive Waste by Accelerator

Lattice Boltzmann simulation of ion and electron transport in lithium ion battery porous electrode during discharge process

Transcription:

Available online at www.sciencedirect.com ScienceDirect Energy Procedia 39 (2013 ) 358 364 Asian Nuclear Prospects 2012 (ANUP2012) Methyl-hydrazine deoxidize Tc(VII) in nitric acid in presence of U(VI) and behavior of technetium in the U/Pu splitting stage of APOR process Abstract LIU Fang*, WANG Hui, JIA Yong-Fen, WEI Yan, ZHOU Yu China Institute of Atomic Energy, Beijing,China The reaction between methyl-hydrazine and Tc(VII) in nitric acid in present of U(VI) was studied in this paper, the influence of acidity, methyl-hydrazine concentration, and temperature on the reaction was investigated meanwhile. Results showed that U(VI) can accelerate this reaction distinctly. When U(VI) concentration is 80 g/l, Tc(VII) can be deoxidized in 1.5 hours, on the contrary, the reaction will last 6 hours if there is no U(VI) in the system. The behavior of technetium in the U/Pu splitting stage was investigated using a multistage mixer-setter. In this experiment about 90% Tc(VII) was deoxidized within 3 stages when contacting with the reducing regent and uranium. Finally nearly 99.9% of technetium went to plutonium stream. 2012 The Authors. Published by Elsevier Ltd. 2013 The Authors. Published by Elsevier Ltd. Open access under CC BY-NC-ND license. Selection and/or peer-review under responsibility of Institute of Nuclear and New Energy Technology, Selection and peer-review under responsibility of Institute of Nuclear and New Energy Technology, Tsinghua University Tsinghua University Keywords: Technetium, methyl-hydrazine, uranium, salt-free, PUREX 1. Introduction A advanced salt-free PUREX process based on organic reductant (abbreviated as APOR process) was explored by China Institute of Atomic Energy, which adopt N,N-dimethylhyldroxylamine(DMHAN) as reducing agent and methyl-hydrazine(mmh) as stabilizer in U/Pu splitting stage and plutonium * LIU Fang. Tel.: 010-69357691 E-mail address: liuxinyu741@sohu.com 1876-6102 2013 The Authors. Published by Elsevier Ltd. Open access under CC BY-NC-ND license. Selection and peer-review under responsibility of Institute of Nuclear and New Energy Technology, Tsinghua University doi:10.1016/j.egypro.2013.07.223

Liu Fang et al. / Energy Procedia 39 ( 2013 ) 358 364 359 purification stage. DMHAN can rapidly reduce Pu(IV) to Pu(III), and MMH acts as HNO 2 scavenger. Pu(III) unloaded from organic phase and separated from uranium[1]. In the U/Pu splitting stage of PUREX process the behavior of technetium is controlled by both its redox characteristics and the partitioning coefficient of Tc(VII). Te(VII) has a moderate partitioning coefficient in TBP/kerosene-HNO 3 system [2-5], but the low valence technetium basically not be extracted, therefore the reaction between technetium and reducing agent has an crucial influence on technetium distribution. The deoxidization of Tc(VII) by MMH in nitric acid is very slow [6]. When c 0 (HNO 3 ) =1.5 mol/l, c 0 (Tc(VII)) =75 mg/l and c 0 (MMH) =0.15 mol/l, it need 6 hours to deoxidize 90% of Tc(VII) to lower valence at 40. Especially in the former 2 hours less than 15% of Tc(VII) was deoxidized. But in the spent nuclear fuel reprocessing process, there is high concentration of uranium and plutonium in the system. The influence of uranium on the reaction has rarely been reported. In this paper, the reaction between technetium and MMH in presence of uranium in nitric acid was detailed studied, further more, the behavior of technetium in the U/Pu splitting stage was investigated using a multistage mixer-setter in order to have a better understanding of the behavior of technetium in this system. 2. Experiment details 2.1. Instruments and reagents Tri-n-butyl phosphate was obtained from Sinopharm chemical regent Ltd., and purified by contacting it with 5% solution of sodium carbonate for the removal of acidic impurities. It was then washed with distilled water until ph = 7. Stock solution of uranium was prepared by dissolving UO 2 pellets with concentrated nitric acid and filtrated before use. Plutonium nitrate solution and neptunium nitrate solution were purified by anion exchange. NH 4 TcO 4 was bought from Oak Ridge National Laboratory and dissolved with distilled water. 2,4,6-Trimethylpyridine was bought from Fluca chemical reagent company. All other chemicals used were of analytical grade. Liquid scintillation spectrometer manufactured by Beckman was used for technetium measurement. 2.2. Analysis Method The concentration of uranium was determined by a potassium dichromate titration method after uranium was reduced to a tetravalent state. Alpha-ray spectrometer was used to determine the concentrations of plutonium. The estimation of free acidity was carried out by titrating suitable aliquot of the sample against standard alkali after complexing the uranium and other hydrolysable ions by potassium oxalate solution using a glass electrode. Liquid scintillation spectrometer was used to detect technetium concentration after technetium was extracted from alkaline solution. 2.3. Experimental Methods The reaction between Tc(VII) and MMH was carried out in a water bath equipment. Bench experiment was done employing a multistage mixer-setter. Flowsheet is shown in Figure 1, process parameters are described in table 1. Fig.1 Flowsheet of U/Pu splitting stage in Bench experiment

360 Liu Fang et al. / Energy Procedia 39 ( 2013 ) 358 364 Tab.1 The process parameters of the Bench experiment stream Content feed stage feed 91.8 g/l U, 0.92 g/l Pu, 0.18 M HNO 3, Tc, Zr, Ru, 30%TBP/kerosene Flux ml/min 7 3.16 Reducing agent 0.1 M C 2 H 6 NOH HNO 3, 0.15 M N 2 H 4 HNO 3, 1 M HNO 3 1 0.79 solvent 0.5 M HNO 3, 30%TBP/kerosene 16 0.79 3. Experiment details 3.1. Influence of uranium on the reaction The reaction between MMH and Tc(VII) in nitric acid with different uranium concentration was studied first. The concentration of heptavalent technetium vs time was showed in Figure 2: Fig.2 The influence of U(VI) on reaction of Tc(VII) and MMH in nitric acid 30,c 0 (Tc(VII))=72 mg/l, c 0 (MMH)=0.15 mol/l, c 0 (HNO 3 )=0.25 mol/l U(VI):1 0 g/l, 2 5 g/l, 3 10 g/l, 4 20 g/l, 5 40 g/l, 6 80 g/l It is obviously that, U(VI) acts a significant role in promoting reaction between the Tc(VII) and MMH, When Tc(VII) concentration is of 80 g/l, the reaction reach equilibrium in 1.5 hours, the Tc(VII) concentration reserve less than 10% of the initial concentration, but in the absence of U(VI), Tc(VII) concentration remained almost unchanged in 6 hours. The deoxidization of heptavalent technetium by MMH went through a similar course as described in literature [7]. The reaction is relatively slow at first which is called induction period, followed by relatively rapid reaction stage called the fast reaction period. It may be a very complicated course [7-9], and the mechanism will not be discussed in this paper. U(VI) promoting the reaction is mainly in shortening the length of the induction period. A higher uranium concentration get a shorter induction period, when U(VI) concentration is 5 g/l, The reaction is not yet entered the fast reaction period within 6 hours; and when the U(VI) concentration is 40 g/l or 80 g/l, there is almost no induction period observed. In contrast, U(VI) has little effect on the fast reaction

Liu Fang et al. / Energy Procedia 39 ( 2013 ) 358 364 361 period, when U(VI) concentration increase from 10 g/l to 80 g/l, the velocity of fast reaction period increased slightly. 3.2. The influence of MMH and acidity The influence of MMH concentration and acidity on the reaction was shown in Figure 3 and 4. The reaction rate accelerated while MMH concentration increasing. Fig.3 The influence of MMH concentration on the reaction c 0 (Tc(VII)) =72 mg/l, c 0 (U(VI)) = 40 g/l, c 0 (HNO 3 ) = 0.25 mol/l c 0 (MMH):1 0.05 mol/l, 2 0.1 mol/l, 3 0.2 mol/l, 4 0.3 mol/l In a certain acidity range, a smaller nitric acid concentration will get a faster reaction rate, but need to ensure an "appropriate" acidity. When the concentration of nitric acid is only 0.05mol/l, the reaction rate slows down, even lower than the acidity of 1.65 mol/l. The acidity of 0.25 mol/l is an "appropriate" acidity in the experiment we did, it may relative with concentration of MMH or other conditions. Tc concentration (mg/l) 80 70 60 50 40 30 20 10 0 0.05 M 0.25 M 0.45 M 0.85 M 1.25 M 1.65 M 0 50 100 150 200 250 300 350 400 time (min) Fig.4 Reaction of Tc(VII) and MMH by different HNO 3 concentration c 0 (Tc(VII)) =72 mg/l, c 0 (U(VI))=40 g/l, c 0 (MMH)=0.15 mol/l

362 Liu Fang et al. / Energy Procedia 39 ( 2013 ) 358 364 3.3. The influence of temperature Reactions in 25, 30, 38, 45 Degrees Celsius were investigated, the data was shown in Figure 5. It can be seen that the temperature has a significant influence, when temperature rising, reaction accelerated remarkably. Fig.5 The influence of temperature on the reaction c 0 (Tc(VII)) =72 mg/l, c 0 (U(VI))=40 g/l, c 0 (MMH) = 0.15 mol/l, c 0 (HNO 3 ) = 0.25 mol/l temperature: 1 25, 2 30, 3 38, 4 45 3.4. The behavior of technetium in U/Pu splitting stage Figure 6 showed the distribution of technetium in each stage of bench experiment when the experiment run for 96 hours. The concentration of technetium in the production of uranium stream which was sampled discontinuously is described in table 2. Tc in aqueous (mg/l) 120 100 80 60 40 20 0 aqu 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 stage org Fig.6 Technetium concentration in each stage of bench experiment 6 5 4 3 2 1 0 Tc in organic (mg/l)

Liu Fang et al. / Energy Procedia 39 ( 2013 ) 358 364 363 Tab.2 Technetium concentration in the production of uranium stream sample Run time, h Concentration of Tc(VII) g/l production of uranium 1 6 2E-6 production of uranium 3 18 6E-7 production of uranium 5 30 3E-6 production of uranium 7 42 2E-6 production of uranium 9 54 5E-7 production of uranium 11 66 3E-7 production of uranium 13 78 2E-6 production of uranium 15 90 2E-6 Seen from figure 6, technetium was reduced to lower valent within 4 stages in the experiment then goes into the aqueous phase. Finally only trace amount technetium goes into the production of uranium stream. More than 99% technetium goes into aqueous phase. The profile of figure 6 was got after the experiment run for 96 hours. It can be supposed that the technetium distribution profile when the experiment just started is very different with figure 5. It may need a long time for each stage accumulating a certain amount of low valent technetium to get a balance state. Though the technetium concentration in the mixer-setter is unstable at the beginning, but we can see that technetium hardly can pass through the back-extract segment of the mixer-setter, the concentration of technetium in production of uranium which was sampled in 6th hour is very low. Technetium concentration in production of plutonium is changed from 0.08 mg/l to 0.19 mg/l, as table 3. It may associate with the running state of the mixer-setter. Tab.3 Technetium concentration in the production of plutonium stream sample Run time, h Concentration of Tc(VII) g/l production of plutonium 1 6 0.168 production of plutonium 3 18 0.187 production of plutonium 5 30 0.101 production of plutonium 7 42 0.160 production of plutonium 9 54 0.086 production of plutonium 11 66 0.079 production of plutonium 13 78 0.174 production of plutonium 15 90 0.144 Tab.4 Concentration of uranium and acidy in each stage stage 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 H +, M 1.4 1.2 1.2 1.1 1.1 1.1 1.0 0.6 0.4 0.4 0.4 0.4 0.4 0.4 0.5 0.4 U, g/l 0.003 0.007 0.03 4 6 24 54 82 77 59 91 90 94 100 91 93 Behavior of technetium in the experiment can be explained as follow: The mixer-setter provides a suitable condition for reducing of technetium. The concentration of uranium and acidy in each stage is expressed as table 4. Contrasting with the kinetics of MMH deoxidize Tc(VII) in nitric acid in presence of U(VI), the system of back-extract segment is very favorable for

364 Liu Fang et al. / Energy Procedia 39 ( 2013 ) 358 364 reducing of technetium, so technetium can be reduced very quickly. And with the accumulating of low valent technetium in each stage, the reaction between Tc(VII) and MMH will start from fast reaction period. About 90% of technetium was reduced within 3 stages. The residual MMH in production of plutonium was determined in the experiment. Result showed less than 50% of MMH was consumed in the mixer-setter. sample Tab.5 Concentration of MMH in production of plutonium MMH, M Reducing agent 0.148 production of plutonium1 0.073 Analyze after sampling 32 hours production of plutonium3 0.079 Analyze after sampling 32 hours production of plutonium4 0.073 Analyze after sampling 8 hours production of plutonium6 0.082 Analyze after sampling 8 hours 4. Conclusion U(VI) can significantly promote the reaction between Tc(VII) and MMH, the reaction get faster when there is a higher uranium concentration. Similarly, increasing MMH concentration, reaction rate is also accelerated. Acidity on the reaction is more complex, there is a suitable acid in the reaction, the acidity is greater than or less than the "appropriate" acidity the reaction will get show. In bench experiment of U/Pu splitting stage about 99.9% of technetium goes into aqueous phase with plutonium. Technetium is reduced very fast within 4 stages. which is due to the suitable acidity and uranium concentration in the U/Pu splitting tank. MMH is consumed less than 50% in the bench experiment. Though MMH is over-consumed than chemometrics, the amount of MMH is sufficient in this experiment. References [1] Hui HE, The application of N,N-dimethyhydroxylamine in the partition of plutonium/uranium and the development of the computer simulation program, Doctor's Thesis of CIAE, 2001. [2] Kolarik, Z., Petrich, G., and Bleyl, H.J., Behaviour oftechnetium in the Extraction with Tributyl Phosphate in the Purex Process, Proc. ISEC 90, Kyoto (Japan), 1990. [3] Kwang Wook Kim, Soo Ho Kim, Kee Chan Song, Extraction and stripping behavior of U Np Tc ternary system to TBP, Journal of Radioanalytical and Nuclear Chemistry, Vol. 253, No. 1 (2002), P.3 10. [4] Dileepa, C. S., Distribution of technetium in PUREX process streams,2nd Biennial Symposium on Emerging Trends in Separation Science and Technology, Volume 232, Issues 1 3, 30 November 2008, P.157 165. [5] Pruett, The solvent extraction of heptavalent technetium and rhenium by tributyl phosphate, ORNL-8668,1984. [6] Fang LIU Behavior of technetium in the U/Pu splitting stage of advanced Purex process, Master's Thesis of CIAE 2009 [7] Garraway, J., Wilson P. D., The Technetium-catalysed Oxidation of Hydrazine by Nitric Acid, Journal of Less Common Metals, Volume 97, 1984, P.191 203. [8] Akopov, G.A., Krinitsyn, A.P., Tsarenko, A.F.,Oxidation of hydrazine in nitric acid solutions in the presence of technetium. Radiokhimiya USSR. (1982), v. 24(4) P. 529-532. [9] LinFeng RAO, Chopin G R. The study of the interaction between perrhenate and uranyl ions, Journal of Nuclear and Radiochemistry. 1987, Vol.9, No.2:76-79