Copyright is owned by the Author of the thesis. Permission is given for a copy to be downloaded by an individual for the purpose of research and private study only. The thesis may not be reproduced elsewhere without the permission of the Author. ANi?LYTICA.L GECYCHEMISTRY ASSOC!i .. TED ELEMENTS IN THE STUDIES ON THE OF URANIUM AND HAWKS CRAG BRECCI1? OF NEW ZEli.Ll'.ND A thesis presented in partial fulfil?ent of the requirements for the degree of Doctor of Philosophy in Chemistry at Massey Univer?ity NOEL EDVU;.RD COHEN 1 969 M All11r(lllil11i i flilii l li li f y 1061960755 ACKNOWLEDGEMENTS The author wishes to thsnk his supervisors, Dr R. R. Brooks and Dr R. D. Reeves, for their enthusiasm and assistance throughout the work undertaken. He is also indebted to Dr G. Coote of the Institute of Nuclear Sciences for his assistnnce in the Gammn Spcctrometry part of the studies; to staff of the Geological Survey for vnlunble advice, to Mr Simon Nath?n, Mr John Foster and Mr Jock Braithwaite for assistance in the field work. He also wishes to thank Mrs Barbara Sanderson for typing the thesis, Miss Doreen Scott for photographic assistance and Mr Peter Herbert for printing the figures. The author is most grateful to the Mineral Resources Sub-Committee of the New Zenland Grants Committee for the provision of funds to support this project. Tl,BLE OF CONTENTS ACKNOWLEDGEJviENTS TABLE OF CONTENTS LIST OF T.r,BLES LIST OF FIGUHES ii.BSTRl?CT GENER?L INTRODUCTION P .. RT I DEVELOPMENT OF i,N1\LYTIC1-1L PROCEDURES INTRODUCTION flN,.LYTICi,L PHOCEDUHES FOl\ THOHIUM , YTTRIUH ,i.ND THE R!.RE Ei.RTH ELEMENTS ( a) Optimum SpectroGraphic Condi tions ( i ) Apparatus ( i i ) Sampl e Preparation ( i i i ) Reduction o f Background I . Investigation o f Carri ers I I . Inves tigation of Gas Condi tions i i vi vii ix 1 4 1 0 10 10 1 0 1 0 10 1 1 (iv) Investigation of S ensi t ivi ty Limi ts 13 ( v) The Volatilisation Behaviour o f Yttrium , Thorium , Lanthanum , Cerium , Europium, Holmium , Palladium, and Zirconium ( vi ) Final Spectrographic Operating Condi tions ( b ) S tudies On The Interference O f Thorium , Y ttrium 15 17 Ana Rare Earth ?nalysis Lines 1 9 t. Development o f an Ion-Exchange Separation 1 9 ( i ) S eparation by Use of the Acet ic/Nitric Acid ?nion-Exchange Syst em 19 (ii) S eparation by Use of the Nitric Aci d hnion-Exchange Sys tem 21 II. Mutual Interference o f Yttrium, Thorium and Rare Earth ?nalysis Lines 21 ( c) The Use of the Combined ?nion-Exchange? Spectrographic Procedure ( i ) Dissolut ion of rlOCk Samples (ii ) Analysis of G-1, W-1 and CAAS Syeni t e ( i i i ) Evaluation o f Data f,N4l.LYTICflL METHODS FOR URf>NIUH (a) Spectrographic Procedure for Macro Amounts of Uranium (b) Solution Fluorimetry ( c) Fusion-Bead Fluorimetry 25 25 27 27 33 33 33 35 DISCUSSION p;,JT II GEOCH;?tnc;,.L INVESTIG"TIONS IN THE Hi,V/I'::S CR,.G BRECCI.h. INTRODUCTION THE GEOLOGIChL ;?ND PHYSICi.L FE.c?.TURES OF THE UR.?,.NIFEROUS :.REf, ( a) Phys i cal Features ( b ) General Geology 37 39 ( c ) The Pe trology and Mineralogy o f the Uranium Deposi ts 44 ( i ) The North Side Depos i ts (ii) The South Bank Deposit? METHODS (a) Sampling Pro c edures ( b ) An?lyt i c al Techniques ( c ) S tatis t ic al ?nalysis of Data ELEl'!ENTi,L ;?SSOCii,TIONS WITH UR!,NIUM IN MINERALS , SOILS riND SEDIMENTS (a) Copper and Uranium ( b) Beryllium and Uranium (c) Lead and Uranium ( d ) Zinc and Uranium ( e ) Rare Earth Elements ELEMENTII.L Ri,TIOS AS p:,THFINDERS FOR UH;?NIUM DISCUSSION PA.HT III MINERf,LS BY EQUILIBRIUM STUDIES HIGH-RESOLUTION GAMMA ON URi.NIUM SPECTROMETRY 46 47 51 51 53 53 56 56 58 58 58 59 64 67 INTRODUCTION 73 INSTRUMENTATION 79 IDENTIFICATION OF SPECTRA 81 ( a) Calibration o f Pulse Height Analyser 81 ( b ) Analys is o f Spec tra 81 (i) 1 80-360 KeV Region 83 ( i i) 30-180 KeV Region 84 EQUILIDRIUH STUDIES ON MINERJ,LS 87 ( a ) Derivation o f th& Equilibrium Relationship 87 ( b ) The Iso topic Compos i t ion o f Uranium Minerals from the Lower Buller Gorge 91 DISCUSSION GEN:Z:Ri?L DISCUSSION HEFE .. n;;NCES 95 98 1 02 LIST OF T;?BLES p,?.RT I I - 1 Effect of Carriers on Line- to-Background Raiio of La4333 i n a Curbon Dioxide htmosphere 1 2 I-2 Times for Com?l?te Volatilisution o f Yt trium? Thorium and Rare Earths in Vari ous Matri ces 1 4 I-3 Line-to-Background R?tios and Limi ts ?f De tec tion for Yttrium , Thorium and Rare Earths 16 I-4 Spe c trographic Oper?t ing Condi t ions 1 8 I-5 Analyti cal Lines and Interferences 24 I-6 Recoveri es from Ion-Exchange Se??rations 28 I-7 Comparison o f Spec trographi c , Neutron hCtivation 29 and Hecommended Values for Thorium , Y t trium , Uranium and the Rare Ear ths i n G- 1 , W- 1 and C:\;?,S Syenite I-8 Rare Earth Abundance Ratios for G- 1 , W-1 and CAAS II- 1 I I-2 II- 3 II-4 I I-5 I I I- 1 I I I -2 Syeni te 30 PU1T I I S tratigraphi c S equence in Lower Buller Gorge Analysi s of S tream S ediments as a Function of Mesh Size 45 52 Statistical Data for Various Elements in Minerals, 57 Soils and S tream S ediments Rare E?rth Conc entrations i n Minerals , Matrix and 60 Stream Sediments Elemental rtatios as Pathfinders for Uranium in 66 S tream Sediments Isotopes and Respective Gamma Ray Energi es used 82 for Calibration of a Pulse Height Analyser The Equilibrium S tate of Various Uranium Minerals 92 from the Lower Bull er Gorge LIST OF FIGURES I - 1 Spec trograms of Rare Enrth Mixtures ( CN band pp 1 2- 1 3 region) Arced in Various Atmospheres I-2 Line- to-background R?t io as a Function o f pp 1 4- 1 5 :trc ing Current I -3 Volatilisation Curves for Rare Earths , pp1 8- 1 9 Yt trium , Palladium and Zirconium I -4 An.:1lysi s ?lement Intensi ty/Palladium Intens i ty pp 1 8- 1 9 as a Function o f the Coeffi c i en t o f Vari?tion I-5 Elution curves for Analysis Elements in Ni trate pp21-22 Sys tem I-6 I-7a I-7b I-8 I - 9 I - 1 0 I-11 I - 1 2 I-13 I- 1 4 Reciproc al Dispersion Ci/mm) and Resolution Ci) pp22-23 as a Function of Wavel ength (R) for the Hilger E742 Quart z-Opti cs Spec trograph ?orking Curves for Cerium ( 4040 ) in the pp25-26 Presence of various c oncentrations o f Neodymium Working Curves for Y 3327 and La 3995 pp25-26 Neutron Ac tivation Data from HASKIN and GEHL pp29-30 as a Funct ion of Spec trographic Data from the Author for G-1 and W- 1 Data from the Author as a Function o f pp29-30 Spe c trographi c Data from TENN.' .. NT and FELLOWS for CAAS Syeni t e Rare Earth Dis tribution for an Average Bas i c pp31-32 Rock and CA?S Syeni t e Spe ctrographi c Working Curve for Uranium pp33-34 Uranium Fluor escence Intens i ty as a Function pp34-35 of Per C ent Phosphori c Aci d Solution Fluorimetry Working Curve for Uranium pp34-35 Fus ion-Bead Fluorime try Working Curve for pp36-37 Uranium Pf .. RT I I I I - 1 Map Showing Dis tribution o f Hawks Crag Brec c ia pp43- 44 on Nes t Coas t of South Island I I-2 II-3a Photo Showing Dense Beech Forest i n H . C . B . Area pp43-44 Aerial Photograph of Lower Buller Gorge including H . C . B . area pp43-44 II-3b II-4 II-5 II-6 II-7 II-8 II-9 II- 1 0 II-1 1 III-1 III-2 III-3 III-4 III-5 I I I-6 III-7 III-8 Aerial Photograph o f H . C . B. Area from Fig . II-3a pp43-44 De tailed Geologi cal Map o f th8 H . C . D . Area pp45-46 Pho tosraph and ,:,u toradiograph of itrkos e pp48-49, containing Uranini te Elemental Relationships in Minerals , Soils pp57-5? and S tream S ediments Cumulative Frequency Plots for Various Elements pp58-59 in Soils and Stream S ediments Rare Earth Distribution i n Uranium Minerals pp59-60 and in Stream Sediments Draining H . C . B . Areas Triangular Plot for C oncentration Ratios of Copper , Lead and Uranium in Minerals, Soils and Stream Se diments Map of Buller Gorge hrea of New Zealand showing Radioactive Horizons and Sampling P oints for Soils and S tream Sediments Triangular Plot for C oncentrati on Ratios o f Lanthanum , Yttrium and Thorium from S tream S e diments in Drainage Areas; Ohika-Nui Riv er , O tututu River and Hawks Crag Brec c ia Pi'.RT III Decay S chemes for u238, u235 and Th232 Comparison o f Uranini t e Spec trum Recorded wi th Nai( Tl ) and Ge ( L i ) Detec tors Gamma Spectroscopy ; Schemat i c Diagram Computer-Assisted Analysis o f Gamma Spec tra; S chemat i c Diagram Calibration Curve , KeV as a Func t i on o f Channel Numb0r Gamma Spe c tra of Uranini t e , Ra226 and Th232 Gamma Spe c tra of Uranyl N i trate , Extrac ted Uranium Fraction and Extrac ted Thorium Frac tion . C(1 85 ) Theoret?cal Curve o f c(295) as a Func tion o f the "Percentage Equilibrium Radium" pp64-65 pp64-65 pp71 -72 pp74-75 pp76-77 pp79-80 pp79- 80 pp81 -82 pp83-84 pp85- 86 pp90-91 hBSTRACT Part I S tudi es were carr i ed out on the opt imum condit ions for the suc cess ful use o f a lnrge quartz spe c trograph for the determin?tion o f thorium , yttrium and the rare ear ths in s il i cat e ro cks . The best l ine-to-background ratios were achieved by arcing samples in a m?trix of 4% sodium chloride in carbon p owder . An atmosphere of 20% argon and 80% oxygen w?s us ed to reduce background and eliminat? cyanogen band int erference . An anion- exchange pro cedure was used to s eparate the rare earths from other elements . The result ing enr i chment allowed use to be made of less sensi tive rare earth lines in the ultraviolet end o f the spe c trum where the spectrograph i c dispersion i s greater . Line interferences w e r e studi ed and nec essary corre c t i ons for thes e interferences were calculate d . The t echnique was tested b y analysing the s tandard rocks , G- 1 , W-1 and CAhS syeni te . Depending on i ts c onc entratio? uranium was analys ed by e i ther fluorametric or spec trographi c te chniques . Good agreem0nt with the recommended values for the s tandard rocks was obtaine d . Part I I An investigation o f the known areas o f uranium minerali zation in the Lower Bul ler Gorge o f New Zealand was carri ed out to i nves tigate the suitab il i ty o f s tream- sediment analysis for geochemi cal prospec ting for uranium . General analysis o f the minerals reveal ed certain el emental associat ions . The distribution of these elements in the weathering sequence, minerals, soils , s tream-sediments , was s tudied in an attempt to dis cover sui table p3.thfinders for ure.nium. ,.11 rcsul ts were tre3.ted s t?tis t i cally . Rare ear th analys i s of s tream sadimants provided new inform?tion concerning the possibl e ori?in of the Hawks Crag Brc:c c ia . P<1.rt I II Us e was made of a high-resolution gamma spcc trometer to s tudy the gamma radiation of uranium minerals in the low energy r egion of the spec trum , 30-360 KeV . Identi fi cation of the gamma radiation , in this region , was achi eved by use of chemi c al s ep3.raticns and s tandard sourc es . This provided the bas i s for the development , and successful us e , o f a new method for the deter? mination of "perc entage equ ilibrium radium" . The s igni fi cance o f the values for the "p erc entage equil ibrium radium" of the minerals s tudied is di s cus s ed . GENER?L INTRODUCTION 1 . In 1 956 , two pros)ec tors , Cassin and Jacobsen , di s covered ur?nium in the Lower Buller Gorge region in the South Island of New Zealand . In the s earch for radioec tive minerals this find was of great geologi cal signi fi cance because i t trans ferred geologi cal thinkin? from the grani tes and associ?ted rocks t o a hi therto unsuspe cted arko s i c b edded formation known as the Hawks Crag Bre c c ia . This discovery by Cassin and Jacobs en s timulated the search for ur3nium i n this area unt il the early 1 960 ' s , when the fall in pri c e of uranium , c ombined w i th unpromising ini t ial findings, made further prosp e c t ing unattractive . R e c ently , as a r esult of Government encouragement , the interest in uranium prosp e c ting has b e en revived and many of the known areas of mineral izati on are be ing re- evaluate d . The need for a source of ur?nium has b e en h eightened because o f the possible ins tallation o f a nuclear r eactor in the lat e 1 970's . Previous i nvestigations have been carried out almos t ent irely b y field geologists and were mainly of ? petrologi c?l nature . In v i ew o f the increasing success o f geochemi cal methods of ex?lorat i0n in other parts of the world , there was c learly a n eed for such an inves tigation i n thi s area. The benefi ts o f such a s tudy would not only be confined to aspects of economi c geology but also provide inform?tion on the history and origin of the uranium de?osits and on the Hawks Crag Brec cia i tsel f . Considering the advantages of geochemi cal obs ervations , i t is somewhat surprising that w i th the exception of work by WODZICKI ( 1 959a , 1 959b ) , l i t tl e or none of this work has been carried out in this area . One possible reason for lack o f work i s that the analyti cal 2. me thods of analysing for urnnium and associated elemants , such as thorium and the rare eGrths , are o f ten tedi8us or unreli able , anu require specialised equipment not generally av?i lable in many? geochemi cal laboratori?s . Provi ded th?t these analyti cnl problems could be solved ?nd a sui table technique could be developed, a geochcmi cal survey of the area would be fac il i tat e d . This thesis desc ribes somewhat intensive investigations into the development of such t echniques and their subsequent a?pli c&t ion to geochemicnl studi es in the H?wks Crag Bre c c ia . WHITEHE?D and BROOKS ( 1 969a ) in reconnaissance work i n the area have highlighted the defi c i encies of many s c intillometri c and o ther radiometric m e thods for the an&lysis of uranium in minerals , soils and s tr eam s ediments . The use of radiometric methods for ac curate quanti tative analysis relies on the assumpti on that the uranium sample i s in radioactive equilibrium . However , ? compre? hens ive s tudy of radioactive equilibrium in thi s are? has never b een satisfac torily at temp t e d , largely because o f the lack o f sui table methods . This problem was there fore investigated as a part o f the present s tudy and has been solved by the appli cation o f ? new t e chnique in gamma spec tromctry . This is reported i n Part I I I of this thesis. To summari?e , the aims of this thesis were threefold : ( 1 ) To develop a ?ethod for the analys is of low concentrati ons of yt trium , thorium and r?re earths wi th the us e of a large quartz? opt i c s spec trograph . (2) To inv es t igate the possible asso ciation o f the above elements , 3nd any other elements , wi th uranium i n the minerals from the South S ide o f the Buller River and to s tudy the dis tribution o f these elements in the weathering s equenc e : minerals , s o ils , s tream- s ediments .? From these results , to examine c r i t i cally the relntive mer i ts of dir e c t analysi s of uranium and of associated el ements in s tream- sediments , a s a geochemical prospec t ing method for uranium minerali zation . (3) To develop a me thod , using only gamma radiation from u235 and Ra226 , to determine the ;'perc entage equilibrium radium" of uranium minerals . DEVELOPMENT OF hN:,LYTIC .. L PHOCEDURES 4 . INTRODUCTION The progress of geochemistry depends ultimately on how effectively the collected quantitative abundance data are utilised. The value of this information is very dependent on the precisi on of the determinations and although it is impossible to assess the quality of each published analysis, an examination of some of the figures provided by the various methods most widely applied, does give an indication of the reliability of much of the existing data. Furthermore, this also gives an i dea of the progress in the analytical procedures which are applied. The classical or conventional methods of rock analysis were fairly well established during the second half of last century ( HILLEBRAND, 1900) and have remained essentially unchanged (WASHIN?TON, 1950; GROVES, 1 951; HILLEBRAND and LUNDELL, 1953). Those who developed the classical procedures, as well as those who used them, frequently attempted to indi cate their accuracy, but no real insight into the quality of this immense collection of published information was gained until FAIRBAIRN ET AL ( 1 95 1 ) organised a world-wide, inter-laboratory investigation on granite (G-1 ) and diabase (W- 1 ) . Numerous analyses of these rocks were carried out by a large number of workers using a wide 9ariety of techniques. The w ide variation in the analytic?l data for i dentical samples clearly demonstrated the shortcomings of many existing analytical techniques. AHRENS (1 957 ) using published data for G- 1 and W-1 , showed that for classi cal procedures, the logarithm of the standard deviation of replicate analyses was inversely related to the logarithm of the concentration of the c onstituent analysed. The signifi cance of this relati onship be comes extremely important when analysing at the trace element ( ppm ) level . For this reason , the analysis of many geochemi cally- important elements such as thorium , uranium , the rare earths and yt trium presents c onsi derable difficulty . Several radiometric me thods have b e en used for the det ermination of uranium and thorium ( EICHHOLZ ET AL , 1 953; CHERRY and ADAMS , 1963; CHERRY , 1 963; HEIR and ROGERS , 1 963; VASS ILAKI ET AL , 1 96 6 ) but these procedures suffer from the dis- advantage that radioactive equilibrium must b e assum ed and this is not always so . Of the above workers , only EICHHOLZ ET AL ( 1 953 ) allowed for this p ossibil i ty . Fluorimetry (GRIMALDI ET AL , 1 952; PRICE ET AL , 1 953; ANDERSON and HERCULES , 1 964) i s undoub tably one of the mos t s ensi tive methods for uranium - 10 ) ( limit o f det e ction 10 g but has the disadvantage that extensive dilution is needed for samples containing even moderate amounts of this element . O ther methods such as emission spe c trography are by contras t extremely insensi tive for uranium . I t i s c lear , therefore that a c ombination o f m e thods i s required i f the conc entrati on range of this element spans several orders o f magnitude . Y t trium , thorium and the rare earths have b e en analysed by X-ray spe c trography ( GAVRILOVA and TURANSKAYA , 1 958; BALASHOV ET AL , 1 964; ALEKSIEV and BOVADJIJ!;VA , 1 966 ) , spark s our c e mass spec trography ( BROWN and WOLSTENHOLME , 1 964; TAYLOR , 1 965; NI.CHOLJS ET AL, 1967 ) , ac tivation analys is ( TOWELL ET AL , 1 965; BRUNFELT and STEINNES , 1 966; COBB , 1 967; GORDON ET AL , 1 96 8 ) and emi ss ion spectrography (FARIS , 1 958; RADWAN ET AL , 1 963; MYKYTIUK 1T AL , 1 966; NELMS and VOGEL , 1 967 ) . The 6 . relative merit of these techniques will b e bri e fly discuss ed for the sake o f c omple teness although only emission spe c trography was available for us e at this ins t i tution . X-ray spe c trography has a relatively poor detection limit making i t generally unsui table . Spark source mass spectrography has been shown to be an accurate and extremely sens i tive t echnique and has the advantage that all elements may be det ermined s imultaneously . Neutron activation i s also extremely s ensitive but requires c onsiderable chemical treatment o f the sampl e to eliminate inter? ference when using the Nai?) detec tor . Direct analysis of the sample can now be achi eved using the recently developed G e (L i ) d e te ctor although "cooling" t imes o f the order o f months are necessary for s ome elements in order to eliminate interference problems . Emission spe c trography has been for many years one o f the most sat i sfacto ry me thods for the analysi s of rare earths in s i l i cates (AHRENS and TAYLOR 196 1 ) . Unfortunately this t echnique nevertheless suffers from certain inherent disadvantages . Thes e are : production o f high background due to the c ompl ex spe c tra of the rare earths; interference from o ther rare earths , t i tanium and i ron ; the necess i ty of high amperages ( FASSEL , 1949; ROSE ET AL, 1 954) and l ong arcing times b ecause of the relative involatility o f the rare ear th oxides . This last fac tor also results in high background due to cyanogen emission in the range 3500-4200 ? where mos t of the best analysis l ines of the rare earths are found . Line interference may also b e reduced by use o f a high- 7. dispersion grating instrument and cyanogen emission may b e controlled by arcing in various nitrogen- free atmospheres such as carbon dioxide (STEADMAN, 1 948) , argon , helium or oxygen ( VALLE? ET AL , 1 950 ) and a mixture of argon and oxygen ( RADNAN , 1 963 ; TENNANT and SEV.IELL , 1 967 ) . Use o f a noble gas atmosphere results i n an enhancement o f ion line i ntensi ti es relative to thos e o f atom lines and a reduction i n background . This is a distinct advantage as the most s ensitive rare earth analysi s lines are i o n lines . The main disadvantage is that arc ing times of the order of minutes are required . Another approach to the problem o f line interference is the carri er distillation method ( SCRIBNER and MULLIN , 1 946; MYKYTIUK ET AL , 1 966 ) which allows arcing times to b e reduc ed by increasing volatilisation rates . To obtain high-pre c ision quantitative results , use o f z irconium ( McCARTY ET AL , 1 938 ) , palladium ( YOUNG , PH . D . THESIS ) and c ertain rare ear ths ( FASSEL and WILHELM , 1 948; Kl'iiSELY ET AL , ? 1 958 ; AHRENS and TAYLOR , 1 96 1 ) as internal s tandards has been recommended . The relatively-high sens i tivi ty o f rare earth analyses referred to in the l iterature ( MITCHELL , 1 948 ; AHRENS and TAYLOR , 1 96 1 ) was obtained via a high-dispersi on i nstrument and cannot b e dupli cated wi th a quar tz- opti cs spectrograph . There is clearly a ne ed for a method whi ch will permit the us e o f such Rn ins trument in rare earth analysi s , particularly as such spe c trographs greatly outnumber grating instruments in general use. The majority of the above techniques require preliminary chemi cal treatment of the sample either to reduce interference or to concentrate the elements being determine d . S eparation methods commonly used are: prec ipitation of r?re earths as hydroxides (ROSE ET AL, 1954) or oxctlates (STEkDMAN, 1948), solvent extraction (l?cCARTY ET AL, 1938; SCRIBNER and MULLIN , 1946; VALLEE ET fL, 1950; RADWAN ET AL, 1963; MYKYTIUK ET AL, 1966) and i on exchange ( CJ._Rm'ELL, 1957; Di\.NON, 1958; NIETZEL 8 . E T AL , 1958; FARIS and WARTON , 1962; FRITZ and GARRALDA , 1962; TAKETATSU, 1963; AHRENS ET AL , 1963; KORKISCH and ARRHENIUS, 1964; S'I'RELOW, 1966) ? It was clear that a s eparation- enrichment procedure would be required for the present work because of line interferences and s ensitivity problems . S eparati on i s parti cularly necessary where samples contain more than five percent uranium , b e cause the presence of a very large number o f uranium lines in the range 2500-5000 E results in a high background i n the emission spectra . This background prevents analysi s of elements other than uranium in thi s range . Prel iminary investigations showed that precipitation and solvent extraction techniques were unsuitable because o f incomplete recover i es . Cation exchange chromatography was un? satisfactory because l?rgc eluting volumes were involved , with a subsequent reduction in the conc entration of the analysi s elements . Anion exch?nge 2ppcared to be the most promising and was i nvestigated further . The f0llowing s e ction reports on the analyti cal pro c edures which were developed for the analysis of uranium , thorium , yttrium and the rare earths i n minerals , s o ils and stream sediments , and involves:- (i) The development of optimum spectrographic operating conditions for the ?nnlysis of yttrium, thorium and the rare earths, using ? medium-dispersion instrument. (ii) Suitable methods for analysing uranium over a concentration range of several orders of magnitude. (iii) The development o f a suitable ion-exchange 9. separation scheme for yttrium, thorium, uranium and rare earths in silicates. ANALYTICAL PROCEDURES FOR THORIUM, YTTRIUM AND THE RARE EARTH ELEMENTS (a) Optimum Spectrographic Conditions (i) Apparatus The experiments were carried out with a Hilger E742 Large Automatic Spectrograph w{th quartz optics (reciprocal dispersion 1 2 E/mm at 4000 ?.) A Hilger microdensitometer with Galvoscale calibrated in B-values (BOSWELL and BROOKS, 1965) was used for densitometry. An image of the arc was focussed on the slit via a quartz spherical lens and the spectra were recorded on Ilford G-30 spectrographic plates developed for 4? minutes in Kodak D 19b developer at 20?. (ii) Sample Preparation In all cases, solutions of thorium, yttrium and rare earths, whether as ion-exch?nge eluants or as pure solutions, were treated in the following standard manner. A quantity of finely-divided carbon powder (50 mg) was added to not more than 50 ml of a solution of thoriu?.yttrium 10. and rare earths contained in a 100 ml beaker. The carbon powder ( 1 20 mesh) contained an added internal standard. After addition of the required amount of carrier, the contents of the beaker were evaporated to dryness at 80? and the dry carbon powder was removed, ground in a motar and loaded into graphite electrodes (cavity 6mm deep and 1.5mm bore) which were dried at 130? for 2 hr. (iii) Reduction of Background I. Investigation of Carriers Preliminary experiments in a carbon dioxide atmosphere 11. were carried out on samples with and without various concentr?tions of each of the following halides: c?esium chloride, silver chloride, sodium chloride and sodium fluoride. Lanthanum was added to each mixture to give a final concentration of 100 ppm and the samples were arced at 12A d.c. using anode excitation. Table I-1 shows the relative intensities of La 4333 to background for the various carriers. From this it is seen that for an atmosphere of carbon dioxide, 4% sodium chloride was the most efficient carrier for a maximum line-to?background ratio. Vclatilisation for a maximum line-to-background ratio was complete in thirty seconds, but the cyanogen emission and background, although less than that without carrier, were still too high. An attempt was made to reduce these further by changing the arcing atmosphere. II. Investigation of Gas Conditions Samples containing a mixture of thorium, yttrium and rare earths in a carbon matrix, with and without addition of 4% sodium chloride, were arced at 12;l (d.c. with anode excitation)successively in air, carbon dioxide and a mixture of argon and oxygen in varying pr0portions from 100% argon to 100% oxygen. This study showed (Fig. I-1) that a mixture of 20% argon and 80% oxygen was the most efficient for reducing cy?nogen emission and background. The samples with s?dium chloride in each case had a lower background than those without carrier but the most striking difference was the considerable reduction of cyanogen emission and background with the 20% argon and 80% oxygen mixture. This level of background was quite acceptable but it was necessary to know whether 4% sodium chloride as carrier and 12:. arcing current were in fact 12. TABLE I - 1 Effect o f Carri ers on Line-to-Background Ratio of La 4333 in a Carbon Dioxide Atmosphere Carrier NaCl NaF AgCl CsCl None 2% 4% 6% 2% 4% 6% 2% 4% 6% 2% 4% 6% In tensity 1. 2 1.7 1. 0 1.3 1.0 0.8 0.5 0.5 0.5 1. 3 1.0 0.8 0.5 ratio A air with 4% sodium chloride matrix B air with carbon matrix C carbon dioxide with 4% sodium chloride matrix D carbon dioxide with carbon matrix E 80 20, 02 Ar mixture with 4% sodium chloride matrix F Bo 20, 02 Ar mixture with carbon matrix Fig. I-1 Spectrograms of rare earth mixtures (CN band region) arced at 10A in various atmospheres. A B c D E F Fig. I-1 Spectrograms of rare earth mixtures (CN band region) arced in various atmospheres. 13. s till the optimum conditions both for background reduction and sens i tivi ty for atmospheres other than carbon dioxi de? It was deci4e d , therefore , t o investigate the aff e c t of di fferent arcing currents , carriers and carri er concentr?tions in the 20% argon and 80% oxygen atmosphere . ( iv ) Investigation o f Sens i tivi ty Limi ts AHRENS and TAILOR ( 1 96 1 ) divi de the rare earth e l ements into three volati l i ty groups . Representative elements ( lanthanum , c erium , europium , holmium , and ytterbium ) from each o f these three groups were taken , as well as yttrium and thorium . Solutions o f thes e elements w ere prepared from their respec tive 1 1Specpure" oxides. Samples containing 100 ppm o f each of thes e metals were prepared in matri ces containing 2%, 4% and 6% sodium chloride , s odium fluoride , caesium chloride and silver chlori de respectively and wi thout carrier . The samples w ere arced at 8A , 1 0A , 12A and 1 4A res?ec tively ( d . c . wi th anode exci tation ) in the 20% argon, 80% oxygen atmosphere wi th the pho tographi? plate being racked down t o expose a fresh area of plate every five seconds. From these volatilisation curves the time taken for compl e t e volatilisation was obtained . The results are given in Table I-2. For the determination of l ine- to-background ratios , a further s e t o f samples i denti cal to those above were arced at 8A, 10A , 12A and 1 4A respectively . Times of arc ing were as in Table I-2r It was obcerved that all carriers increased the line-to-background ratio and improved th? detec tion l imi t of each element at each of the di fferent concentrations of carri er us ed as compared with no carrier . Within each carri er conc entration range , this e ffe ct usually increas ed t o ? maximum at 1 0A and 12A decreasing again at ? ..::t TABLE I - 2 ....- Times for C omp l e t e Volat i l isation o f Y t trium , Thorium and Rare Earths i n Various Matr i c es Carri er NaCl NaF ilgCl CsCl No Carrier 2% 4% 6% 2% 4% 6% 2% 49'; 6% 2% 4% 6% I Volatilisation time(sec) at 8 amp 35 30 25 25 25 30 20 25 25 30 30 30 35 : \I " " it 11 " " 1 0 11 30 25 25 20 20 25 25 20 20 30 25 30 35 11 11 n " 11 11 11 1 2 " 30 25 20 ? 20 20 25 25 25 20 25 30 30 35 ll " " " il " " 1 4 il 25 25 20 1 5 1 5 20 25 20 20 25 30 25 35 8 10 12 14 Amps Fig, I - 2 Line-to?background ratio as a function of arcing current. 15. 14A ( Fig . I-2) . I t was observed, that 4'76 sodium chloride and 6% sodium chlori de at 10A and 1 2a ?espectively provided the largest increas e in the l ine-to-background rati o and improvement in the detection limit for every element as c ompared with no carrier . Results obtained under thesG conditions are shown in Table I-3. The limit of d etection is taken arbitarily to b e that conc entration o f the e l ement whi ch will give a line intensi ty equal to that of the background . Since the average background intens iti es were of the order o f 50 B-value units , the limit of detection was taken as that concentration which would give a value o f 50 B-value units for the line i ntensity after correction for background. Table I-3 shows that almost i denti cal r esults were obtained with e i ther 4% o r 6% s odium chloride arc ed at b o th 10A and 1 2A respectively. The final choi c e of carrier concentration and arcing amperage was determined by the relative volatilisation rates of the analysi s elements and internal standard . F6r accurate , quantitative results i t is essential that the behaviour o f the analysis elements and i nternal standard be as similar as possibl e. As zirconium and palladium had been used by other authors (McCARTY ET AL, 1938; YOUNG , PH.D. THESIS) it was dec ided to inves t igatG their suitabili ty under these conditions. (v) The Volatilisation Behavi our of Yttrium, Thorium, Lanthanum , Cerium, Europium, Holmium, Palladium and Zirconium Samples c ontaining 100 ppm of thorium , yttrium and each o f the above rare earths end 1000 ppm o f palladium and zirconium were prepared in matrices containing 4% and 6% sodium chloride resp ectively . Each sample containing a part i cular concentration o f carri er was arced at 10A and 1 2A in the 20% &rgon , 80% oxygen TABLE I - 3 Line- to-Background Ratios and L imi ts o f D e te c tion for Yt trium , Thorium and Rare Enrths Carri er 4% NaCl 6% NaCl A B A B - - - - Yb3289 at 1 0 amp 22 . 2 0 . 6 36 . 0 0 . 6 at 1 2 amp 33 . 8 0 . 6 48 . 0 0 . 4 Ho3456 at 10 amp 9 . 67 1 . 5 9 . 5 3 . 0 at 1 2 amp 9 . 00 1 . 5 1 2 . 6 3 . 0 Y37 1 0 a t 1 0 amp 1 3 . 4 0 . 8 1 4 . 1 1 . 5 at 1 2 amp 1 3 . 5 0 . 8 1 7 . 4 0 . 8 Th40 1 9 at 1 0 amp 4 . 65 5 . 0 4 . 0 6 at 1 2 amp 3 . 47 5 . 0 3 . 2 ? 5 Eu41 29 at 1 0 amp 9 . 00 1 . 5 9 . 6 3 at 1 2 amp 8 . 00 1 . 5 8 . 8 1 . 5 C e4 1 33 at 1 0 amp 0 . 8 1 1 2 . 5 0 . 84 1 2 . 5 at 1 2 amp 0 . 52 9 . 0 o . 8o 1 2 . 5 La4333 at 1 0 amp 1 . 78 6 1 ? 4 9 at 1 2 amp 1 . 54 6 1 . 7 6 h Line- to-background ratio 1 6 . No Carrier A B - - 4 . 2 5 6 . 2 5 2 . 2 9 2 . 3 6 2 . 9 5 3 . 1 5 1 . 4 9 1 . 4 6 1 . 2 9 1 . 0 9 0 . 1 25 0 . 2 25 0 . 5 1 3 0 . 2 1 3 B Limit o f d e t e c t ion ppm ( relative line intens i ti es greater than 50 B-value uni ts ) . 17 . atmosphere and suc cessive exposures were made at fiv& s e cond intervals . The curves obtained arc shown in Fig . I-3 . This figure shows that palladium was , in all cases , a better element than zirconium for use as an internal s tandard as i t follows the V?Jlati lisation behaviour of the analysi s elemEnts more clos ely . The optimum arcing amperage is 10A with 4% sodium chloride as carr i er , b?cause unc er these condi tions ?ll the e l ements exc ept zirconium have volatili Ged comple tely wi thin t?enty five seconds wi thout becoming too d i fferentiated . Thi s reason renders the o ther cond i ti ons less sui table . ( vi ) Final Spec trographi c Operating Cortdi tione . ? Table I - 4 gives the final condi tio?s chosen as a resul t of the abo ?,r e investigations . The reproducibili ty o f the spec trographic analysis using these condi tions was determined in the following manner . A s eries of standards containing thorium , y ttritim and ra?e earthe w i th a wide concentration were prepared and arced under the abo?e condi tidns . Ten repli cate arcings wore made at each concentration l evel . The analy": i s l ine intensi ty o f each el ement and that o f the internal standard palladium , was m?asured over the ctincentration range and the ratio of the two was determined . This ratio was plot ted aga1rist the c oeffi c i ent o f variation ( percent s tandard deviation ) and is shown . in Fig. I - 4 . This curve allows tho c o effi c i ent of variati on to be determined for ?ny e lement at any conc entration and i s more meaningful than the v?luc obtained from a singl e d e t ermination . The usual pr?cedure in such work is to calculate the coefficient of vari ation from repli cate analys es o f an element a t an eas ily measurable concentrati on . This nuturally pres ents valu&s bet ter -------- -- - --- 18 . TABJ?E I - 4 Spe c trographic Op erating Condi tions S l i t l ength S l i t width Wavelength range Pho tographi c plates Current Excitat ion Exposute Ele c trodes Photographi c Process ing Op ti cal sys t em Arc gap Gas 1 2 mm 0 . 0 1 5 mm 2800 - 5000 9 ,.. I l ford G-30 1 0h d . c . !?node 25 s econds Johnson-Matthey 4B graphite ( 1 . 5 mm internal diameter x 6 mm de ep ) 4? min at 20?C in Kodak 1 9B developer Ima?e o f arc focussed at s l i t w i th F95B convex quartz l ens 4 mm 20% argon/80% oxygen = ..... - .... ..... - .... = ... N 50 Fig , I - 3 4 % NaC I - 1 0 A 6 I. NaCI - 10 l Y O L A T I L I S A T I O N 30 T 1 1 E C U R V E S S E C S . 4 % NaC I - 1 2 l 6 1. hCI - 12 l 10 20 Volatilizat ion curves for rare earths , yttrium , palladium and zirconium . 30 4 Fig . I - 4 Coeff ic ient Of Va r iat ion % Analysis element intensity/Palladium intensity as a function of the coefficient of variat ion . than can be ob tained at lo?er concentrat ion l evels . ( b ) S tudies on the I nterference o f Thorium , Y t trium and Rare Ear th Analysis Lines I . Development of an Ion Exchange S eparation 1 9 . ( i ) S eparation by Use of the Ac e t i c/Nitr i c A c id Ani on - Exchange Sys t em Solutions were pr epared containing macro elements in the propor?ions fo und i n grani te ( G- 1 ) as given by FLEISCHER ( 1 965 ) and 1 000 ppm each o f uranium , thorium , yttrium and the rare earths . The solvent was a mixture of 90% glac ial ac e t i c acid ?1d 1 0% nitri c ac i d . The anion- exchange procedure used was a modi fication o f work reported by KORKISCH and ARRHENIUS ( 1 964 ) . The m e thod used was as follows : Res i n : Dowex 1 x 8 ( 1 00 mesh ) , chloride form . Column Dimension : 1 5cm x 1 cm. Flow Rate : 0 . 5 - 0 . 7 ml/min . The column was prepared in the normal manner as described by VOGEL ( 1 96 1 ) and c onverted to the ni trate form by passing 5 M nitr i c acid until the eluant no longer gave a pos i t ive t e s t t o s ilver ni trate . The column was then equilibrat ed w i th 45 ml of a mixture o f 90% glac ial ac e t i c acid and 1 0% 5 M ni tri c acid which had previously been degassed on a water pump . The previously prepared mixture of elements , in the same solvent , was passed through the c olumn followed by 50 ml of the same solvent to r emove any weakly-adsorbed &lements . Yttrium , thorium , uranium ?nd the 20 . rare earths remained adsorbed on the resin . Uranium was s eparated fro? thorium , yttrium and the rare earths by eluting with 35 ml of 6 M hydrochlori c aci d . Thi s converted the uranium into a chloro- complex whi ch remained adsorbed on the c olumn whereas yttrium , thorium and the rare earths were eluted ns they do not form strong chloro- complexes . The uranium was then eluted w ith 25 ml o f 0 . 1 M hydrochlori c aci d . The s eparation took approximately five hours , but several columns could be run s imultaneously . I n thi s cas e a battery of s i x was found to be suitable . S everal experiments were carri ed out to i nvestigate the e ffe ct o f flow rate and element concentratio n , especially uranium , on the s eparation proc edure . It was found that the s eparati on effi c i ency was unaffected by flow rates varying b etween 0 . 2 ml/min and 1 ml/min . The factor governing flow rate was actually the room temperature as the a c etic a c id b ecame rather viscous around 1 8? C . In most cases the flow rate was between 0 . 5 ml/min and 0 . 7 ml/min . For the column dimensions given , it was found that s olutions samples containing up to 2500 ppm uranium were suc c ess? fully s eparated . Element recovery exp eriments were also perfJrmed to determine the effi ci ency o f the s eparation . The r esults obtained indi c ated that there was mutual i nter ference i n the rare earth emissi on sp ectra , becaus e many elements gave apparent concentrations much higher than the amounts added woul d hav e i ndi cated . Although the above s eparati on suc c ess fully conc entrates the analysi s el ements and removes interference from macro c onstituents , there still exists mutual interference from the rare enrths themselves . Results o f anion exchange s eparations r ep -- ?rted by CARS?vELL ( 1 957 ) and DANON ( 1 958 ) indicated that i t 2 1 . might be possible to s eparate uranium , thorium , yt trium and rare earths into several groups , hence reducing interference . The following i nves tigation was c arried out . ( i i ) S eparation by Use of the N i tric A c id Ani on? Exchange System Uranium , thorium , y t trium and rare earths were adsorbed on to the c olumn , as described i n the above s e c tion , and w?re , in s eparat e experiments , eluted w i th 2 M, 4 M and 6 M ni tric aci d r espe c tively ( flow rate 0 . 5 ml/min . ) . Aliquots o f 5 ml w ere taken ov er a volume o f 1 20 ml . Results o f these s eparations are shown i n Fig . I - 5 . From this i t i s s een th?t the s eparati on i s unsatisfac tory and further att?mpts a t s eparat ion were di s continue d . I t i s poss ibl e to s eparate the rare earths using ammonium ci trate as eluting agent ( SPEDDING ET AL , 1 950 ) but the time i nvolved r endered this approach unsat is fac tory . An examinat ion o f line sp ec tra o f the analysis elements was then made in an attemp t to determine the extent of mutual line i nterference of thorium , yttrium and the rare earths , so that these el ements might be analysed together as a group . The following results are e s s ent iRlly thos e reported by COHEN ET AL ( 1 968 ) . I I . Mutual Interference o f Yttrium, Thorium and Rare Earth J>nalysis Lines In this s tudy it was necessary to know how the resolut ion o f the large quart z spec trograph vari ed with wavelength . Thi s was determined in two s teps . Firstly , a curve of r ec ipro cal dispersion ( ?/mm ) agains t wavelength C R ) was cons truc ted from the NBS card index by m0asuring the distance ( mm ) apart o f any two lines at en +"' ?- s:::: ::J >. +"' ? -(/) s:::: Cl) +"' c: - >. ... ro ...... ?- .c ... <( 0 0 1 ?0 Yb , y , Nd , Eu Gd ' Ho , Dy I 6 M Sm Er ' \ Ce .... ..... .. ,. --.. ----y--.. ,, .... .. ,, ., .. .. ; "', '..., ,' , .... , ..... , L U ? - ... .. ..., , ' '\ ,'' .. , ,' ..... , ....... a , .. ' ... .. .. ... I ,,, 'I" ", , .. , ' ,' " ' ' I I ' I " ' ,. ' ,; ' .. .. ' , ? ,' "' , '"' ...... ,., No Th detected .. ? , ., ', ... ....... , "" , ,' '? ' ' ,-, ,... ,"" I , ' ? ' .... ,.. ,.. ( lnt en?:ntl. e s ) range A ( from Fig . I-6 ) Lu 2 9 1 1 . 39 ( 600 ) + 0 . 1 8 Yb 3289 . 37 ( 2600 ) ? 0 . 27 Tb 3324 . 40 ( 400 ) ? 0 . 27 y 3327 . 89 ( 600 ) ? 0 . 27 Pd 342 1 . 24 ( 1 400 ) * * ? 0 . 30 Gd 3422 . 57 ( 700 ) ? 0 . 30 Ho 3456 . 00 ( 1 800 ) ? 0 . 31 Tm 3462 . 20 ( 800 ) ? 0 . 32 Dy 3531 . 70 ( 2000 ) ? 0 . 33 Er 3692 . 64 ( 700 ) ? 0 . 38 La 3995 . 75 ( 360 ) + 0 . 48 Th 40 1 9 . 1 3 ( 300 ) ? 0 . 50 Ce 4040 . 76 ( 1 50 ) :t 0 . 50 Nd 406 1 . 09 ( 280 ) :t 0 . 50 Pr 4 1 79 . 42 ( 460 ) ? 0 . 55 ?u 4205 . 05 ( 4000 ) .?. 0 . 57 Sm 4256 . 38 ( 1 40 ) .?. 0 . 59 * Int ens i t i e s from NBS Tabl es * * Internal S t ?ndard Interfering l ines in ? ( intens i ti0s ) * Th 291 1 ? 32 ( 8 ) None None None None None None None None None None Ce 40 1 9 . 04 ( 1 4 ) N d 4o4o . 8o ( 1 8o ) None Ce 41 79 . 29 ( 5 ) None Ce 4256 . 1 6 ( 1 2 ) Intensity ratios o f inter- fering lines and reference lines Th 29 1 1/Th40 1 9 = 0 . 027 None None None None None None None None None None Ce 40 1 9/Ce 4o4o = 0 . 237 Nd 4040/Nd4061 = 0 . 732 None I C e 41 79/Ce40 1 9 = 0 . 07 6 None C e 4256/Cc4o4o = 0 . 092 2 5 . correc ted c erium intens i ty at 4040. 76 R is obtained by subtrac t ing 73% o f the neodymium intsnsi ty at 406 1 . 09 ? ( interference fre e ) from the observed value for the c erium l ine . The correc tion o f analysis lines for interferenc e should be carri ed out in the following s equenc e . C e 4040 i s corre c ted for Nd 4040 interference , followed by correct ion of Th 401 9 for Ce 40 1 9 , using the corrected Ce 4040 intens i ty value to c al culate the corr e c t value for Ce 40 1 9 . Having obtained interferenc e- free Ce 4040 and Th 401 9 intens i t i es , Pr 4 1 79 c ?n b e c orre c t e d for ? n?e>dymium , c erium and thorium interferences . Working curves for interferenc e- free elements can be prepared by dilution of a c ommon mixed s tandar d , but o ther working curves mus t be prepared from indivi dual unmixed s tandards . Fig . I-7a shows the working curve for Ce 4040 in the presence o f various conc entrations of neodymium , with and wi thout corre ction , and the curve obtained from a pure c erium s t ?ndnrd . Working curves for o ther elements (Fig . I-7b ) are also given . The l ow s catter o f the points gives an indi cation o f the pre ci sion of the m e thod . ( c ) The Use of the Combined Anion Exchange? Spe c trographi c Proc edure ( i ) Dissolution o f Rock Samples The ease w i th which rocks are dissolved dep ends primari ly on the n?ture of the rock ( s ili cate , sulphide e t c . ) , the elements present, and the solvent use d . The solvent required for the anion exchange s eparation , i n this cas e , governed this cho i c e and henc e presented c ertain di ffi cul ties . The main one was that 90% glacial a ce t i c a c id and 1 0% 5 M ni tri c ac id i s an extremely poor solvent . 1? 00 0?10 1 0 Fig , I - 7a C e r i um a Ce Nd = 1 1 b Ce Nd = 3 1 C P,ure Ce cl Corrected A and B curves for Nd interference 1 00 }J9 Working curves for cerium ( 4040 ) in the presence of various concentrations of neodymium . y 3327 L a 3 995 1 0 1 00 ).1 9 Fig . I - 7b Working curves for Y3327 and La3995 . 26 . Also , the el ements thorium and c e rium are generally very insoluble even in mineral acids . As a result , the following rather t edi ous scheme had to be used . Concentrated nitric acid and concentrated hydrofluoric acids ( 1 5 ml o f each ) were added to 1 g o f finely- divided rock sample ( 1 20 mesh ) in a 250 ml te flon beaker nnd evaporated to dryness over a p eri od o f 2-3 hr . Then 1 5 ml o f c oncentrated nitri c acid was added to the residue , whi ch was next transferred to a 1 50 ml glass beaker and slowly evaporated to dryness. To this residue was added 1 5 ml of 9 : 1 mixture o f glaci al aceti c acid and 5 M ni tr i c ac i d , and the whole was transferred to a tube and c entrifuged . The supernatant l i quid was retained and the residue was again treated w i th 1 5 ml of c onc entrated nitric Rcid , evaporated to dryness , taken up in 1 5 ml of ace t i c acid-ni tric acid mixture and c entr i fuged . The solution was retained and the residue (usually less than 0.3 g) was dri e d , weighed , mixed in a 1 : 3 rat io w i th sodium p eroxide and fused in a platinum c rucibl 2 at 480? for s even minut es (RAFTER , 1 950 ? . The melt was neutralised w i th nitric acid and the solu tion centri fuged . Any solid remaining was dis carded . Suffi c i en t glacial ncetic acid to give the c orrect ratio o f acetic acid t o ni tri c aci d was added and all three supernatants w er e combine d . The total vulumc was usually 70-80 ml . The solution was degassed for twenty minutes and then tr?nsferred to the prepared ion- exchange column . Complete digestion o f the nnalysis elements was confirmed by arcing the supernatants and residue of a t est sample after each s tage had been completed . 27 . ( i i ) Analysis of G- 1 , W - 1 and CAAS Syeni te To evaluate the complete an?lyti cal pro c edure , experiments were carried out to test the recovery of elements from the ion? exchange column . Table I-6 shows the results ob tained for some representat ive el ements c arri ed through a complete s ep?ration and analysi s procedure . Analysi s o f the standard rocks G- 1 , W- 1 and CA?S Syeni t e for thorium , yttrium and rare earths was carried out by the developed proc edure . Tabl e I -7 compares the resul ts ob t?ined w i th the mos t recent r?commended values . ( i i i ) Evaluation o f Data The agreement b e tween the spec trographic results obtained in this work for G- 1 and W- 1 and tho?e given by FLEISCHER ( 1 969 ) are go od . The neutron ac t ivation data o f HASKIN and GEHL ( 1 963 ) als o correlates extremely well and i s shown in Fig. I-8 . The values obtained for CAAS Syeni t e give fresh data for nine rare earth elements whos e vcl.ues , as r eported by WEBBER ( 1 96 4 ) were e i ther doubtful o r were below t h e d e te c tion limi t o f the t e chniques us e d . The rec ent summary of SIN? ET AL ( 1 969 ) includes v?lues obt?ined by TENNANT and FELLOWS ( 1 967 ) , also using emission spectrography . These values generally correlate well w i th this work and are shown in Fig . I-9 . Thi s figures shows that there i s disagreement i n t h e values for samarium , holmium and lut e c ium . I n order to evaluate the c orrectness of t h e values obtained , the r?re earth abundanc e ratios for an average acidi c ro ck , a n average bas i c rock and C?AS Sye? t e were calculated . These values are given i n Table I-8 . ? ?i s t able shows that whenever the results o f this work and those o f Tennant and Fellows agree , the abundance ratio ( normal i s ed t o La = 1 . 00 ) o f the rare earths in the sye nite 28 . TABLE I - 6 Recoveries from I on-Exchange Separ?tions El ement J>moun t added (fl.g ) ,'-?mount recovered ( ?g ) La 300 280 Ce 300 309 Nd 300 309 Sm 1 00 1 02 Eu 1 00 98 Gd 1 00 99 Dy 1 00 1 02 Ho 1 00 1 02 y 1 00 1 00 . 0' (\j TABLE I - 7 CoQparison o f Sp e c trographi c , Neutron Activation and Recommended Values for Thoriua, Yttrium , Uranium and the Rare earths i n G- 1 , W- 1 and ChhS Syenite ( ppm ) Element G- 1 W-1 Crti.S Sy?ni t c Code A B c D l'l c D .a B E La 1 1 00 80 100 1 02 1 0 1 2 1 1 . 7 1 8? Zlf5 220 Ce 2 200 1 60 1 70 1 34 20 23 24 350 625 365 Pr 3 1 9 1 6 1 7 20 . 9 5 4 3 . 68 1 37 1 40 - Ncl 4 60 43 55 54 . 6 16 1 7 1 5 . 1 300 305 302 Sm 5 < 5 c: 1 0 9 8 . 6 ? 5 4 3 . 79 4:. 5 245 - Eu 6 0 . 9 1 1 . 3 1 . 04 1 . 5 1 ? 1 1 . 09 1 5 8 - Gd 7 7 <: 1 0 5 4 . 88 4 4 4 . 2 72 58 - Tb 8 < 2 < 50 0 . 6 0 . 5 < 2 0 . 8 0 . 75 ? 2 4: 50 - Dy 9 2 < 20 2 . 5 n . d . 2 4 n . d . 1 00 1 35 - Ho 1 0 0 . 4 < 1 0 . 5 0 . 5 3 1 1 . 35 2 1 2 - Er 1 1 1 . 4 <. 1 0 2 1 . 4 2 . 5 3 2 . 57 57 42 - Tm 1 2 < 3 <: 1 0 . 2 0 . 2 < 3 0 . 3 0 . 35 < 3 5 - Yb 1 3 0 . 6 0 . 8 1 0 . 62 1 . 5 2 . 2 2 . 1 90 57 70 Lu 1 4 0 . 1 .c 1 0 0 . 2 0 . 1 7 0 . 3 0 . 35 0 . 33 1 . 5 < 1 0 - y 1 5 1 2 1 2 1 3 1 2 . 5 1 1 25 23 . 8 450 450 450 Th 30 2 1 52 n . d . 1 2 . 4 n . d . 710 1 300 1 338 u 2 . 6 < 50 4 n . d . 1 . 5 0 . 5 n . d . 2380 2700 2500 fl - This work . B - Dire c t :':lr c ing w i th high dispersion instrument ( TZNN/?NT and FELLO';?s , 1 967 ) . C - Recommended values for G- 1 and W- 1 (FL.SISCHER , 1 969) . D - Neutron activ :>. t ion ( }bSKIN and GEHL , 1 963) . E - Median values for CArlS syenite ( SINE ET tL , 1 969 ) . n . d . - Not determined . I E 0. 0. c 0 .. nJ > .. (J n sour c e . Exc i tation w?vel ength : 264 m? Emission wavel ength : 5 1 3 mp 34 . From Fig . I-1 2 i t i s s e en that 5% or 1 0% phosphoric ac i d i s the optfmu? phosphoric a c id conc entration . All fur ther analysi s were carried out us ing 1 0% phosphoric ac i d . Preliminary working curves were prepared and i t was found that Beer ' s Law was obeyed up to about 13 ppm uranium . To increase the appli cable c onc entration range , the following dilution s cheme was developed . Solutions with 5 ?g - 50 pg of uranium were diluted to 5 ml w i th 1 0% phosphoric ac i d , samples w i th 25 pg - 250 ?g were diluted to 25 ml and amounts o f 250 ?g - 1 000 )lg required dilution to 1 00 ml . The results are shown in Fig . I - 1 3 . This allowed each analysis t o b e carr i e d o u t in such a way thut i f dilution was necessary , the total uranium pres ent , and no t a frac tion of i t , was diluted . This con? s iderably reduced the absolut e error in the analys i s due to dilution . The analysi s was carr i e d out as follows : The i on-exchange eluate c ontaining only urani um was taken to dryness , 5 ml of phosphor i c acid was added and the solution was examined under an ul tra violet lamp ( 254 m? ) . I f the fluores c ence intens i ty was too high this volume was further dilut ed to 25 ml and again examin?d . I f the intens i ty was s t i ll too high after diluting to a volume o f 1 00 ml , then a frac tion o f this was t aken and diluted further . However , thi s s i tuation was unc ommon . en .... ? - s::: 8 0 ::J ? +J en c Q) +J s::: - ? ? cu +J ? - .c ? a ? ea +"' ? - .c ? ffini te ) . Soil samples w ere taken from various points on the dr?inage slop es o f the South Bank horizons and were air drie d , pas s ed through a 40-mesh nylon sieve anu then igni ted at 450?C to remove the organic mat ter . Further grinding to 1 00-mesh followed . S tream sediments were coll e c t ed from various s treams draining ond adjoining the urani ferous areas on the South Bank in the following manner . Samples were taken from s tream deposits and were wet-si eveG through a 40-mesh , nylon cloth stretched over the mouth o f a plast i c funnel . The fraction passing the s i eve was collec ted in a plast i c bag and the fines were allowed to settle for approximately two to three minutes before the water was decant ed o f f . The posi tion of the sampling point and the bng marking was noted . The sedim2nts were dri ed at 1 1 0?C and separat ed into three frac tions by the use o f nylon s ieves . The frac tions were : less than 80 mesh , between 60 and 80 mesh , and between 40 and 60 mesh . Preliminary analysis of these fractions showed that the "less than 80 mesh" c ontained the highest conc entration of nearly all el ements investigated (Tabl e II-2 ) . Sample B 1 BC4 T.4BLE I I - 2 hnalysi s o f S tream Sediments as a Function of Mesh Size Mesh Size La Ce Pr Nd Gd Dy Yb Less than 80 54 1 34 1 5 34 1 3 4 . 8 4 . 1 B etween 60 and 80 36 67 1 0 1 4 8 . 5 2 . 7 2 . 3 Between 40 and 60 42 95 1 3 1 6 8 . 5 3 . 8 2 . 4 Less than 8o 26 50 1 1 9 7 2 . 3 1 . 0 Between 60 and 8o 20 44 1 2 1 1 4 . 6 1 . 7 1 . 1 B etween 40 and 60 2 . 8 40 2 1 2 3 . 2 0 . 4 0 . 5 52 . y Th u 1 2 . 5 1 1 1 3 . 6 1 4 1 1 1 0 . 0 2 1 1 4 9 . 8 4 . 8 3 . 1 4 . 8 5 . 6 6 . 0 4 . 8 1 1 3 . 8 53 . ( b ) ?nalyti cal Techniques Emi s sion spec trography was used to an?lyse beryllium , thorium , uranium , yttrium and rare earths as described in Part I . Solution fluorime try and p ellet fluorimetry were used to analys e uranium , the parti cular m e thod used depending on the uranium conc entration . A Techtron Ah3 atomi c absorption spe ctropho tometer was used to analyse copper , zinc ?nd l ead . The sample was treated w i th a m ixture of hydrofluori c and hydrochloric aci ds and taken to dryness . The residue was redissolved in 2 M hydro chloric ac i d , filtered and stored i n plas t i c bot tles until the t ime o f analys i s . ( c ) Statis t i cal Analysis of Dita To be abl e to make careful int erpretation of the int er? element analyti cal results , correlation c alculations were c arried out on a IBM 1 620 ( I I ) computer . Correlations between two variables are usually c arr i e d out by the method o f l inear regress ion , but MIDDLETON ( 1 963 ) notes that this i s applied to determine whether one variable is dependent on the o ther when the latter is not sub j e c t to error . However , in this work , as in most geochomi cal work , neither variable can be said to be absolut ely known . Therefore , i t is b e t ter to c alculate the reduced maj or axis , rather than the regression l ines . The advantages of the reduced major ? axi s are that : 1 . i t makes no assumptions of independence ; 2 . i t is invari ent under change o f s c al e ; 3 . i t i s s imple t o c ompute ; 4 . results obtained from i ts us e are intui tively more 54 . reasonable than corresponding resul ts obtained from regr ession analys is . ( IMBRIE , 1 956 ) . For all thes e correlations , the logari thms o f concentrations 0 were compared , since the conc entrations often spanned s everal orders of magni tude and appeared to be log-normally dis tributed ( AHRENS , 1 954 ) . Thus the posi tion o f the reduced major axis on a log-log bas i s , was calculated for each pair o f analyti cal data , and the s igni fi cance of the correlation determined by c al culation o f the correlation coeffic ient ( r ) and reference t o the tables o f FISCHER and YATES ( 1 957 ) ? . . Cumulative frequency s tudies of some o f the data were also carried out . A plot of the cumulative frequency of the concentrations o f the samples , as a perc entage of the total number of s amples , plotted on probabili ty paper agains t the concentration value , has been shown to be useful for geochemi cal and biogeochemi cal data interpretation ( TENNANT and WHITE , 1 959 ; WILLIAMS , 1 967c ) . In parti cular , l og-normal dis tributions will show a straight line when plo t ted on log-probability paper , and similarly w i th normally- distributed data on linear-probabil ity paper . In o thei cases , curves will ensue . However , i f there i s more than one dis tribution s e t wi thin the data , such a s could o ccur in mineralized and unmineralized soil samples , a dist inc t change o f slope or a poin? of inflexion in the graph will b e observed . This break can b e consi dered t o oc cur a t the minimum concentration of mineralized samples , al though some overlap o f dis tributions will oc cur (WILLI?MS , 1 967c ) . I t mus t b e remembered that the s ignifi cance o f interpretation from this analysis is 55 . somewhat limited unless the set contains about 80 to 1 00 samples . However , generalised conclus ions can be obtained on sets less than 80 . ELEMENTAL ASSOCIATIONS WITH UR?NIUM IN MINERALS , SOILS AND SEDD1ENTS This s ection reports on the v?rious elemental assoc iations w i th ur?nium and discusses their sui tab ility as pathfinders . Thi s i s essentially the same as was reported by COHEN ET AL ( 1 969 ) . ( a ) Copper and Uranium 56 . Analysi s of copper and uranium in mineral s , soils and L) s tream s ediments , combined w i th a s tatisti cal i nterpretation o f the dat a , showed a meaningful correlation between this pair o f elements for the whole of the weathering s equenc e minerals - soils - s tream s e diments . Correlation coeffic i ents are shown in Table II-3 and plot s o f the data are shown in Fig . II-6 . Correlation coefficients decrease regularly in the s equ8nc e minerals - soils - stream s e diments and indicate that ass o ciat i on between this pair of elements originates i n the minerals and i s preserved throughout the weathering s equenc e . WHITTLE ( 1 960 ) has obs erved that chalcopyri te i s assoc iated w i th tiranium in the South Bank depos its o f the Lower Buller Gorge and thi s is probably the source of the c opper det e c ted . Further m obilisation and transport of both elements i s fac ili tated by the porous nature of the arkosic matrix whi ch allows oxidation and movement to take place . The pres ervation o f the ini t i al copper-uranium relati onship throughout the whol e weathering s equence is a fortunate o c currence whi ch renders c opper a useful pathfinder i n minerals , soils and s ediments . Cumulative frequency plots for c opper i n soils and . ['-. li\ TABLE I I - 3 S tat i s t i cal Data for Vari ous Elements i n Minerals , Soils and S tream Sediments Firs t C orrelati ng S e c ond Correlating Minerals Soils Sediments Variable Variable Log concn . o f U L o g c oncn . Log concn . o f U Log concn . Log o oncn . o f U L o g concn . Log c oncn . o f U Log concn . Log c oncn . o f Cu Log concn . Log c oncn . o f Cu Log concn . r = c orrelation c o e f f i ci ent Si g . = l evel of s igni fi cance of Be of Cu of Pb of Zn of Pb o f Zn r 0 . 88 0 . 79 0 . 95 0 . 02 0 . 78 0 . 04 S i g . r Sig. r - - S * * 0 . 68 s ? ? o . o? S * * 0 . 66 s ? ? 0 , 42 S * * o . 8o s? ? -0 . 25 NS 0 . 34 PS 0. 1 2 S * * 0 . 74 s ? ? -0 , 1 4 NS 0 . 32 PS 0. 20 N . B . Levels o f s ignif i can c e ( BROOKS ET AL , 1 96 6 ) shown above are as follows : S * * = s i gnifi can t at 0 . 1 % l evel o f probab i l i ty ( very highly significant) S* = s igni fi c an? a t 0 . 1 - 1% level of probab i l i ty ( h ighly signi ficant ) S = s ignifi cant at 1 -5% l evel of probabil i ty ( si gnifi cant ) PS = s igni fi can t a t 5- 1 0% level o f probabil i ty ( possibly signifi cant ) NS = no t s ign i fi can t Sig . NS PS NS NS NS NS P.eM. u 100,000 10poo 1/) _, < a: w z ? 1000 P.P.M. U c:! 100 0 1/) 10 P.I?M. U u - cu ? 20 10 1/) 1- z w ? 0 w 1/) . ? 20 ttM. Cu Fig . II - 6 U - Pb ? ? ? ? ? 10 100 ? ? ? ? . ? ? ? ? ? ? 10 Pl'M. Pb ? ? ? ? ? ? ? ? ? ? ? ? ? ? ? ? ? ? ? ? ? P.P.M. Be Elemental Relat ionships in Minerals , Soils and Stream Sediments . ? ? 10 10 --------- - -- 58 . s ediments ( Fi g . II-7 ) show that anomalous amounts c orrespond t o greater than 60 ppm i n soils and greater than 40 ppm in sediments . Such values may repres ent indire c tly the presence o f uranium mineralization . ( b ) Beryllium and Uranium Statisti cal analysis of beryllium and uranium data showed a meaningful correlation b e tween this pair of elements in the minerals , and soils but not in the s tream s ediments . Correlation c o e ffic i ents are given in Table II-3 and plots of the data are shown in Fig. I I- 6 . Cumulative frequency plots for the soils are shown i n Fig . II-7 , from whi ch it i s s een that b eryllium (j values above 4 ppm ( normal background distribution for grani t i c rocks ) i ndi cate abnormal values and would sugges t th e presence o f uranium . ( c ) Lead and Uranium The association o f l ead wi th uranium in the minerals i s extremely c lose ( Table I I -3 and Fig . II-6 ) . The correlation is so good ( r = 0 . 95 ) that the author believes that mos t o f the lead is radiogeni c in nature . In the soils , two dis tinc t distributi ;ns are evident (Fi g . I I-7 ) and a value o f 70 ppm appears t o indi cate the threshold value for anomalous l ead . The correlation b e tween uranium and this element in soils is still good ( r = 0 . 80 ) but not as good as in the minerals whereas in the s tream sediments no c o rrelati on b e tween these elements exis ts at all . ( d ) Zinc and Uranium - No s igni fi cant correlati on was obs erved for this pair of . P.P.I. A B Fig . II - 7 2 5 1 0 20 30 .40 50 60 70 80 150 PPm C U M U L A T I VE P.P.I c. c D E F R EQ U E N C Y ? ? .40 ppm 2 5 10 20 ? .40 50 tll 70 80 98 99 . 99?8 Cumulative Frequency Plots for Various Elements in Soils and Stream Sediments . A - Uranium in soils B - Lead in soils C - Beryllium in soils D - ? Copper in soils E - Copper in sediments 59 . e l ements in minerals or s ediments ( Table I I -3 ) but there was a poss ibly- signifi cant relationship in soils ( r = 0 . 34 ) . A z inc- uranium relationship in soils has also been obs erved by WHITEHEAD and BROOKS ( 1 969b ) . How ever , the author cons i ders zinc as an unsui table pathfinder for uranium since the value of r is s o low . ( e ) R?re Earth Elements The analysis of minerals for y t trium , thorium and the rare earth el ements was carried ou t using the analyt i cal proc edure described in Part I of this thes i s . The r esults ore shown in Table I I- 4 . Thi s table shows that although the l evels of these elements are slightly higher in the mineralized fraction c ompared 0 wi th the unmineralized frac ti on , they are s t ill extremely low . However , desp i t e their low conc entration , the normal Oddo-Harkins dis tribution exis ts , ( Fig II-?, that i s , the even- ) numbered rare earths have a h i gher conc entration than the uneven numbers and thus show that no frac t ionation has o c curred wi thin the group . S tatisti cal analysis o f the data was not at tempted as i n most c ases the conc entration of the el ements was almos t a t the d e te c tion limi t . Visual inspection o f the results show that there are no meaningful correlations b e tween any of the el ements and uranium and thus yt trium , thorium and the rare earths are unsui table as pathfinders . Ho?ever , the low valuas obtained are s igni ficant in them- selves as they sugges t that e i ther the original uranium was not asso c iated w i th rare earths or that the uranium has b e en mob i l i s ed and because of the greater solub i l i ty o f uranium ( VI ) c ompare d . :!: a: 0.: M inera ls M inera l i zed Frac t ion ,JJ., lit 'JJ. Unm inera l i zed Fraction Stream Sed i ments 1 ? Var iat ion a ro u nd mean 1 La Ce Pr Nd Pm Sm Eu Gd Tb Dy Ho E r Tm Yb Lu Fig . I I - 8 Rare Earth Distribution in Uranium Minerals and in Stream Sediments Draining Hawks Crag Breccia Areas . ? 0 \.0 TABLE II - 4 Rare Earth Con?entrations i n Minerals t Matrix and Stream Sediments (ppm ) Sample La Ce Pr Nd Sm Gd Dy Yb y Th u - -- MINERilLS Uranini t e 1 1 0 1 8 n . f . n . f . n . f . 7 1 . 5 1 . 4 8 . 5 4 1 62 , 000 Matrix 1 6 8 n . f . n . f . n . f . 2 0 . 9 0 . 5 1 . 0 n . f . 1 0 , 000 Uro.nini te 2 7 19 n . f . n . f . n . f . 8 . 5 0 . 6 3 . 0 1 4 . 0 n. f . 1 20 , 000 fhtrix 2 7 8 n . f . n . f . n . f . 6 . 5 1 ? 1 0 . 8 3 . 4 n .? f . 1 0 , 000 Uranini t e 3 n . f . n . f" ? n . f . n . f . n . f . 9 . 5 4 . 4 4 . 4 9 . 5 n .. f . 1 10 , 000 Mntrix .3 n . f . n . t?. n . f . n . f . n . f . n . f . 0 . 9 0 . 9 1 . 9 n . f . 248 Matrix 4 1 9 n . f . n . f . n . f . n . f . n . f . n . f . 0 . 8 n . f . n. f. 843 Torb e?itic ) 3 1 42 n. f . 30 n . f . 6 . 5 n . f . 1 . 8 4 . 8 n .. f . 750 Mntr?x 5 i\utuniti c ) Matrix 6 4 n . f . n . f . n . f . n . f . 5 . 9 1 . 7 1 . 7 6 . 5 n. f . 8 Gummite n . f . n . f . n . f . n . f . n . f . n. f. n . f . n . f . n . f . n . f . 250 , 000 STREAN SEDINENTS 01 28 50 1 4 1 7 n . f . n . f . 1 . 6 1 . 0 2 . 5 4 . 6 3 . 4 02 47 95 1 8 40 n . f . n . f . 4 . 8 1 . 6 1 2 1 8 8 .6 03 28 54 1 2 1 1 1 0 3- 7 2 . 2 0. 6 3 . 4 5 . 6 2 . 4 04 1 6 26 5 1 0 n . f . n . f . 0 . 6 0 . 1 1 . 9 3 . 4 2 . 0 05 30 40 1 3 1 6 8 3 . 6 2 . 7 1 . 0 6 . 0 7 . 0 1 . 2 1 4 4 . 0 ' 4 . 5 07 1 5 25 1 0 n . f . 11. f ? 0 . 7 0 . 5 1 . 5 08 30 38 1 1 . 0 1 6 . 0 9 . 0 4 .0 2 . 4 0 . 9 6 . 0 6 . 0 3 . 4 B 1 3 23 46 1 2 1 1 n . f . 5 . 0 2 . 5 2 . 0 8 . 0 5 . 4 8 . 6 B 1 4 20 30 10 7 n . f . 3 . 6 0 . 8 1 . 2 2 . 6 6 . 4 0. 8 B 1 5 26 45 9 1 1 n . f . 5 . 6 1 . 3 0 . 7 5 6 . 4 2 . 9 B 1 6 54 1 34 1 5 34 n . f . 1 3 4 . 8 4 . 1 1 2 . 5 1 1 . 0 13 . 6 B 1 7 27 57 1 2 1 9 4 1 2 . 0 0 . 9 6 . 5 4 . 8 1 . 4 B1 8 42 60 1 8 30 n . f . 8 . 5 2 . 4 1 . 3 1 6 9 1 . 7 'I""" \() TABLE I I - 4 continued S ampl e Ln Ce STREAM SEDIM?NTS cont . BR1 29 BR2 46 BR3 45 BC 1 25 BC2 2 6 BC3 30 BC4 26 BC5 28 n . f . not found . 90 70 6 1 46 52 60 50 74 Pr 1 0 1 4 1 0 1 0 1 2 1 4 1 1 1 5 Nd Sm n . f . n . f . 30 1 0 36 1 2 1 3 n . f . 1 5 n . f . 22 n . f . 9 4 1 5 6 Gd Dy Yb y Th 3 . 4 n . f . 1 . 5 4 . 8 1 7 1 1 . 5 2 . 5 0 . 8 9 . 0 1 6 1 0 3 . 6 1 . 5 1 3 . 0 1 1 1 2 1 . 5 0 . 7 4 6 . 0 7 1 . 8 0 . 7 4 . 4 5 . 6 9 2 . 6 1 . 1 6 . 0 6 . 5 7 2 . 3 1 . 0 4 . 8 3 . 1 6 2 . 3 o . B 4 . 4 5 . 0 01 represents sample 1 from the Ohika- i t i River as shown in Fig . II-9 . B1 3 represents sample 1 3 from Tiroroa Creek as shown i n Fig . I I-9 . BR represents Big River area ( Fi g . I I - 1 ) . BC repr esents Bullock Creek area (F ig . I I- 1 ) . Uranini t e 1 , 2 and 3 represent thr e e di fferent mineral sampl?s and Matrix 1 , 2 and 3 represent the assoc iated matrix fraction ( Fi g . II-5 ) . u 8 . 8 0 . 8 0 . 4 ! 6 . 8 4 . 0 i 3 . 8 4 . 8 4 . 0 6 2 . w i th rare earths , frac tionation has taken plac e . This lat t er reason is beli eved to be more l ikely as mineralogical s tudies by WHITTLE ( 1 960) have also shown evidence for the epigenet i c nature of uranium . During the current investigation , TENNANT and SEWELL ( 1 967 ) published the results of a survey of the rare earth contents in s tream s ediments o f the adj acent O tu tu tu River and Ohika-Nui River no t including the Hawks Crag Bre c c ia drainage are a . These results showed that the Otutu tu area was rich in " c erium- earths" whereas t he Ohika-Nui River area was r i ch in "yttrium- earths " . The conc entration range o f the elements Lanthanum , C erium , Neodymium , Yttrium and Thorium varied from s everal tens to several hundred ppm . This variati'on was generally unpredi c table as element concentrations from samples taken wi thin s ev eral hundred yards of each other could vary by an order o f magni tud e . Overall , however , the rare ear th pat t ern for each area was qui te dis tinc t ive . The Hawks Crag Bre c c ia is found on b o th sides o f the Ohika-Nui River and O tututu River ( Fig . I I- 1 ) and al though it is generally believed that it has no t travelled very far , due t o the pres enc e of angular parent rock , i ts origin is s till far from clear . P etrologi cal c omparisons of the grani tes in the Brecci a wi th those in neighbouring areas s e ems t o sugges t that the Brec cia could p ossibly be derived from the O tututu grani t e ( NhTHAN , pers . cornm . ) . I t was hoped that analyses o f s tream s edirnents from the Hawks Cra.g Brec c ia would r e fl e c t characteris t i c rare ear th pat t erns whi ch when c ompared w i th tho s e obtained by TENNANT and SEWELL might show whether the Breccia c ould have b e en derived from e i ther the Ohik?-Nui granite o r the Otututu granite or possibly both . The results obtained ?re shown in Table II-4 and are discussed later . ---?---------------------- 64 . ELEMENTAL Ri,TIOS i\.S P .. THFINDEHS FOR UR'"'NIUM From Fig . I I -7 i t appears that an anomalous uranium dis tribution may b e detected by the pres ence of > 70 ppm lead , "> 4 ppm beryllium and > 60 ppm copper i n the soils and >40 ppm cop?er in the s tream sediments . Although the analysis of s tream s ediments for copper as a pathfinder for uranium appears to be a likely m e thod , the possib i l i ty of s ingle anomalous copper values due to o ther fac tors i s s ti ll a danger to the reliabil i ty of the metho d . For this reason vari ous ratios and combination o f ratios o f all the associ ated elements were investigated in an attempt to es tablish a more reliable crit erion for the detection of anomalous areas . The use of ratios or c ombination of ratios tends to l e ssen I the importanc e of any spurious , anomalous resul t . Figure I I -9 shows a triangular plot for uranium , l ead and copper concentrat ions in whi ch each const i tuent is expressed as a perc entage o f the ?urn of the three . The data are there fore not based on the absolute perc entage of each element in tho enti re mineral , s o il or s tream-s ediment sample . 1l decreas e in the uranium content i ndi cates the progress ion o f weathering through the s equence minerals- soils-s tream sed iments . I t i s s een that in the s ediments , the uranium content de creases t o very low values and the importance of the l ead- copper relationship becomes much great er . Visual insp ec tion of the data for the s tream s ediments in Fig . II- 9 , shows that there is a t endency for c ertain samples to b e grouped toge ther in the copper-r i ch corner of the graph . Thi s implies higher copper/lead rati os , part i cularly for s ediments 1 0 , 1 3 , 1 5 , 1 6 and 1 7 , the sampling positions of whi ch arc shown i n Fig . I I- 1 0 ? 1 3 100% Cu Fig . II - 9 100% u ... ... 16 ... M INERALS H IGHLY-M INERAL ISED SO I LS UNMIN. SEDTS . 8 ? 3 5 7 12 .,. - So i ls 1 , 2, 3,- ? ? -Sediments 11 100%Pb Triangular Plot for Concentrat ion Ratios of Copper , Lead and Uranium in M inerals , Soils and Stream Sediments , 11 ' I I Fig . I I - 10 N r A A A RAD IOACTIVE AR EAS ? SOIL SAMPLING AREAS 0 NEW RADIOACTIVE AREA SCAL E : 1 inch : 700yds ltap of Buller Gorge Area of New Zealand showing Radioactive Horizons and Sampling Points for Soils , and Stream Sediments ? -------------- ---- --- --------? The copper/l ead ratios are shown also in Table II-5 whi ch includes the uranium c ontent and indicates whether the s tream from whi ch the sample was taken (Fig . I I- 1 0 ) was known to drain a uranium anomaly . hs far as was known at the time , Tiroroa Creek ( sampl e 1 0 ) was not known to drain a radioac tive area . As i t s eemed that higher copper/lead ratios in s tream s ediments might in?i cate uranium anomali es in the drainage area o f . the s tream , further sampling was carried out in Tiroroa Creek. These samples gave further evidence of uranium mineral i zation in this area wi th absolute uranium values ranging from 1 8- 62 ppm and w i th associated hi gh copper/lead ratios . No . 1 2 3 4 5 6 7 8 9 1 0 1 1 1 2 1 3 1 4 1 5 1 6 1 7 1 8 TJ:..BLE II - 5 Elemental Ratios as Pathfinders for Uranium in Stream Sediments Name o f Stream Cu/Pb ratio u concn . ( ppm ) Trib . Ohika- i ti R . 0 . 42 3 . 4 Main Stream - 0 . 58 8 . 6 Ohika- i t i R . Trib . Ohik3.-i t i R . 0 . 44 2 . 4 Trib . Ohika- iti R . 0 . 42 2 . 0 Trib . Ohika- i ti R . 0 . 44 1 . 2 Tri b . Ohika- iti R . 0 . 73 4 . 3 Trib . Ohikn- i t i R . 0 . 36 4 . 5 Trib . Ohika-i ti R . 0 . 44 3 . 4 Trib . Ohika- iti R . 0 . 70 1 . 6 Trib . Ohika- i ti R . 0 . 80* 0 . 8 Trib . Ohika- iti R . 0 . 1 8 3 . 4 Trib . Ohika-iti R . 0 . 25 1 . 5 Tiroroa Creek 7 . 69* 8 . 6 Batty Creek 0 . 67 0 . 8 Big Tick Creek 0 . 83* 2 . 9 Centre Creek 2 . 27 * 1 3 . 6 Hawks Crag Creek 0 . 83* 1 . 4 Blackwater R . 0 . 70 1 . 7 66 . Vvhether mineral- i zation previously known No No No No No No No No No Yes No No No * * Doubtful Yes Yes Yes No * Ratio indi cating presenc e o f minerali zation in drainage area. * * Evidence o f mineral i zation found at later date . 67 DISCUSSION Geochemi cal prospec ting i s conc erned w i th the detec t i on o f ? anomalous amounts of any element as a guide to the d etection o f i ts ore . Thi s problem may essentially be appro?ched in two ways i Samples collected from a grid survey may be analys ed e i ther directly for the element conc erned or for its assoc iated elements ? The cho i c e o f e i thGr o f these two appro?ches depends on the answers to the following ques tions . Firs tly , is the me tal being sought capable of b eing transported far enough from its source and in suffi c i ent quanti ties , to j us t i fy direct geochemi cal s earch? S e condly , will normal variations in the background of the area render any geochemi cal method unreliable . In view o f these questions , pathfinder elements. may b e defined as elements whi ch , b e cause o f s ome parti cular property or properties , provide anomali e s or halos more r eadily usuable than the sought-after element with whi ch they are assoc iated . Uranium i s well known for i t s solubil i ty and extreme mobility and as d iscussed previously , i s a di ffi cul t element to prosp e c t for dire c tly in areas ' o f rugged topography and high rainfall . Hence the impor tant role o f p?thfinders i n this ins tance . However , i t i s interesting to note that Table I I-4 shows a uranium value whi ch i s dis t inctly higher i n a sample from a known mineraliz ed stream ( B 1 6 , C entre Creek ) and thre e other high values ( Big River 1 , Tiroroa Creek LB127 and Ohika- i ti River L027) . I t was found that BR 1 was taken thirty yards down? s tream from an i solated uranium anomaly ( FOSTER , p ers . comm . ) and more detailed investi gation in Tiroroa Creek indicated a general radiation l evel two or three tim2s background . The sample from the Ohika- i t i River was taken in the main stream and the high value 68 . obtained is thought to be due to an unrepresentative fraction . ?11 these anomalies detected by the d ir e c t ?nalysis of uranium have two features in common . These are : ,1 ) the sample taken was very close ( wi thin fi fty yards ) of the uranium anomaly , and 2 ) the uranium anomaly was a cons iderable part o f the drainage area and regis tered at leas t three t imes above background on a s c intillometer . Although dir e c t analysi s of uranium in s tream-sediments regist ered some succ ess , this survey has shown that generally ?n an area of rugged topography and high rainfall this approach is unsui table . S tat i s t i cal evaluation o f the elements associated wi th uranium throughout the weathering s equence minerals , soils , s tream-s e diments , show ed that only copper was suitable as a path? finder in the s tream-sediments whereas l ead , b eryllium and copper were suitable pathfinders i n minerals and soils . To unders tand these results i t i s necessary to CJns ider the different w eathering pro cesses involved and to evaluate their relative s i gni ficanc e . Three main types o f weathering may b e distinguished : physi cal , chemi cal and biologi cal . Phys i c al proc esses include those that c ause rock disintegrati on wi thout appreciRble chemi c al or min?ralogi cal changes . As the rock disintegrates , the sur face area b e comes larger and this facili tates chemi cal w eathering due to reac tions w i th water , o xygen and carbon dioxid e . Biologi cal ac tivi ty c an contribute e i ther direc tly or indirec tly to both phys i cal and chemi cal weathering . G0nerally , thes e pro c es s e s t ake place s i de by side and their relative importance vari es according to the environment . I n the Buller Gorge region , although the to pography i s rugged and the annual rainfall i s high , both condi ti ons being sui table for physi cal weathering , the area is dens ely covered with vegetation whose natural rain shield and large root ne twork successfully prevents erosion . Thi s dens e vegetation cover may also play an important role in the b iological weathering process as uptake o f elements such as copper , zinc and uranium by the flora has been shown to be qui t e s ignifi cant (WHITEHEAD and BROOKS f 1 969b ) . Although b iologi cal effects can make an appreciable contribution to the overall weathering pro cess , as does physi cal weathering , the author feels that the c ontribution of this effect i s low as the levels o f element concentrations found i n the s o il " are too high to have accumulated from decayed vegatation . Evaluation o f the e ff e c t of physi cal and biologi cal w eathering processes for the d istribution o f the elements indicates that the largest cont!ibution comes from chemi cal weathering . Acc ep tance th?t chemi cal weathering is the maj o r fac tor i s s trengthened when i t i s remembered that the Hawks Crag Breccia is a porous sands tone matrix and as a result o f the high rainfall , oxi dation and transport of the soluble e l ements is easily facili tated . 0 A comparison of the solubi li ties of the elements uranium , copp er , lead and beryllium shows that uranium ( VI ) is the most soluble followed by copper , l ead and then beryllium . Further evi dence substantiating the importanc e of chemi cal weathering i s 70 . shown by the fac t that b e caus e o f solub i l i ty differences , l e ad and b eryll ium do no t correlat e wi th uranium beyond the soils whereas c opp er do es . Because copper i s less s o luble than uranium i t i s m o r e sui tab l e f o r analys i s in s tr e am- s ediments than t h i s element and i s henc e a sui table pathfinding element for uranium . ?nalys is o f uranium minerals for yttrium , thorium and the rare ear ths did not provi de any us e ful i nforma tion conc erning possible pathfinders for uranium . I n all cas es the levels o f the s e el em ents i n the minerali zed r ocks were extremely l ow , w i th the levels i n the minerali zed frac t i on be ing slightly high e r than tho s e in the unmineral ised frac tion . S tream s e diment concentrations were higher again and probably r e fl e c t the greater prop o r t i on of grani t i c mat erial in the Br e e c i a . The resul ts presented i n Tabl e I I - 4 f o r t h e analys i s o f s tr eam s ediments from t h e Hawks Crag Bre c c i a for yttrium , thorium and rare e ar ths show that overall the concentrations of these e l ements are low compared w i th the majority o f those values ob tained by TENNANT and SEWELL from the Otututu and Ohika-Nui grani t i c areas . The generally low levels ob tained for yttrium , thorium and the rare earths are probably du e to dilution w i ?h the w eathered matrix mat erial whi ch , as shown by resul ts in Tabl e I I - 4 for the matrix , i s d e f i c i ent i n rare G ar ths . An a t t emp t was made to compare the rare earth d i s t ributi ons found in the Hawks Crag Bre c c i a areas wi th thos e found i n the Ohika-Nui and Otututu River areas b y computing the amounts of lanthanum , yttrium and thorium in each samp l e as a perc entage o f the sum o f the thre e , and by p l o t ting these values on tri angular graph paper . The elements , lanthanum yt trium and thnrium w?re chosen b e c aus e they were shown by TBNN.!?NT and SE'.'JELL 7 1 . to be the most discriminating for the r espe c tive areas . F ig . I I - 1 1 shows the r esults obtaine d . The overlap o f samples from the Ohika-Nui area into that area on the graph representing the O tututu area and v i c e versa , i s a result o f the fluc tuat i on o f the element concentration wi thin each area . I t i s s een however , that the greates t concentration o f samples from both the Ohika-Nui and O tututu areas do fall into s eparate ?reas on the graph which may be taken as 1 1 c haracterising11 that part i cular area sampled . I t i s c l early seen th?t the samples from the Hawks Crag Breccia fall closer to the area charact erised as Otututu than that c harac terised as Ohika-Nui River . This would indi cate that the Hawks Crag Brec c ia was derived from the O tututu grani t e . The author consi ders , how 0ver , that for a more definite indication of this relationship , analysis o f a large number o f samples from all the Hawks Crag Bre ccia areas would be required . I n summary , i t i s c oncluded that this work has shown that i n the Hawks Crag Breccia ar ea , prosp e cting for uranium by us e o f pathfinder elements , l ead , b eryll ium and c opper in soils and c opper in s tream sediments provi des a relatively speedy and s imple m e thod . Dir e c t analysi s for uranium was shown to be , i n general , unsui table unless the sampling s i t e was close t o the radioac tive area . Although yttrium , thorium and rare earths did no t prove sui table as pathfinders for uranium , the analysi s o f stream sediments for these elements did provide new evidence to support the suggestion that the Hawks Crag Bre c c ia was derived from grani t e from the O tututu area . The uncertainty concerning this origin is refl e c ted i n the various theories for the origin of the uranium mineral i zat ioJl. 100%Th Fig , II - 11 0 ? D (,? D l OO% La 0 CJ) ? ? ? ? ?0? ? 0 ? D ? ? ? ? ? ? ? ?? ? ? ? ? ? ? ? ? ? Oh i ka - Nu i ? Otu tu t u ? D B ig R iv e r ? Bu l ler ? ? Bu l l o ck C r ee k ? 0 Oh i ka - i t i ? ? ? ? ? ? ? Triangular Plot for Concentration Ratios of Lanthanum , Yttrium and Thorium from Stream Sediments in Drainage Areas ; Ohika-Nui. River , Otututu River , and Hawks Crag Breccia , lOO% V H. C. B. 72 . i ts elf ( BECK ET AL , 1 958 ; WODZICKI , 1 959b ) . The final par t o f t h e thesi s inter ali a reports on low energy gammR ray s tudies carried out w i th the minerals t o d e termine their c omposi tion and s tate o f equilibrium ; an impor tant cons i deration for any discussion conc erning the origin of these radi oactive deposi t s . EQUILJBRIUM STUDIES ON URi-iNIUM MINZRALS ? BY HIGH.-RESOLUTION a;LMHA SPECTROMETRY and 73 . INTRODUCTION Natural ur?nium , cons i s t ing of 99 . 28? u238 , 0 . 7 1% u235 . 234 . 0 . 0 1% U , 1 s an unstable element whose i s 0 topes decay t o s impler nucli des w i th emiss ion o f alpha , b e tn and gamm? radiation . The recording o f this radioactivity w i th appropriate elec troni c ins truments has , f or many years , b een a c onvenient method f or the dGt e c tion of uranium and has formed the basis of 0 method used extensively in exploration for uranium mineral i zation . At firs t , hand-borne Geiger-Muller counters , whi ch detect alpha and beta radiation , w ere us ed , but these instruments have now been super- s eded by the more s ensi t iv e s c intillome ter . The s c inti llometer detects gamma radiation , whi ch i s considerably more energet i c than ?lpha or beta radiation , and hence fac ili tat es detec tion of radio- ac t ive substances at a much greater r?nge than do es the Geiger count er . B e caus e o f the hi ?her sens i tivi ty achieved , the s c intillomet er can be operated from moving v ehic l es . The lat e s t dev elapm?nt in radiometric survey t e chniques i s the use of highly-sensi t ive s c intillometers capable of di fferentiating b e tween 40 radiations from uranium , thorium and K ? I t i s well known that the maj or fraction o f gamma radiation o f the uranium series comes from the decay o f daughter products o f Ra226 ? An approximate det ermination of the amount of uranium present can be made directly from the measurement o f the gamma radiation i f i t i s assumed that the mineral is in radioac tive equi librium . In thi s , i t is implied that the rate of produc t ion of Ra226 from u238 must equal the rate o f decay of Ra226 , a c ondi t ion whi ch i s no t always satisfied in practi c e . For the purpose of ore de te c t ion , however , where we are conc erned wi th the 74 . order o f magni tude o f the uranium concentration , the state o f equilibrium is unimpor tant . ?s i t has baen found that many uranium minerals are not in equilibrium , di rec t measurement o f the gamma radiation for uranium c .nt ent leads to incorrect values . This probl em can be overcome by measuring both beta and gamma radiati0n ( ZICHHOLZ ET ?1 , 1 953 ) . However , the importanc e o f knowing the s tat e o f equi librium o f a uranium min2rQl is no t confined to the qu nti tative analysis o f uranium . In order to obtain the age o f a uranium mineral it i s also ne c essary to know i ts state o f equilibrium , as deviations from the equilibrium st?te ch?nge the Pb206;u238 or Pb207;u235 r?tios . ( Pb206 and Pb207 are the s table end products o f the decay o f u238 and u235 respectively , as shown in Fig . I I I - 1 ) . The t erm generally acc ep ted t o describe the s tate of equilibrium o f a uranium minerc:-.1 i s npercentnge equilibrium r .?tdium " . Thi s is defined ?s the amount o f radium ac tu?lly present i n a sample e xpressed ?s ? perc entage o f the amount of r?dium whi ch would b e present if a state n f radioac tive equilibrium existed between the uranium and the products o f i ts d e cay . ts has b e en ment i oned previously , this s t?ge is reached when the rat e o f radium decay becomes equ&l to the rate of radium formation . There are tw :.> m::t in re-=tsons for the 1 1p erc en to.ge equilibri urn radi urn" devi[t ting frnm one hundred p erc ent . ( a ) Insuffi c i ent time may have elapsed since tho d 0 ?osit i nn c f the uranium t o allow tho form?t ion o f the equi librium amount o f radium . The rate at which the Ra226 activity builds up to that o f the u238 parent is limi ted by the hal f-l i fe of one of the intermediate members of the s eri0s , u234 ( ti = 2 . 0 . 1 05 yr ) . Only Element Uranium I Uranium x1 Uranium x2 Uranium ri ? Ionium Rad ium Radon Rad ium A ? Rad ium B I Astfitine Radium c I Radium c ? I ? Radium C" I Radium D Radium E I Radium F I Thallium ,.:: I Radium G ( end produc t ) El ement Ac tinouranium Uranium Y Protac tinium Ac tinium ==-----1 Radioactinium I Ac tinium Ac tinium X Actinon Ac t inium A I Ac t inium B I .Astatine 4! I Ac t inium ? .? Ac tinium I Ac tinium I A t " '!E D c :t.n:t.um ( end produc t ) Fig. III-1 K C " Uranium Series ?-'--'??-- Symbol 238u 234Th 234 Pa 234 . u 230T? 226 Ra 222Rn 2 1 8Po 2 1 4Pb 2 1 8At 2 1 4Bi 2 1 4Po 2 1 0Tl 2 1 0Pb 2 1 0Bi 2 1 0p0 206Tl 206Pb Actinium Series Symbol 235u 231 Th 231 Pa 227Ac 227Th 223Fr 223Ra 2 1 9An 2 1 5p0 2 1 1 Pb 2 1 5At 2 1 1 Bi 2 1 1 Po 207Tl 207Pb Rad iat ion a. ? ? a. a. a. a. a. , ? j3 a. j3 , a. a. ? ? ? , a. a. ? - Radiation a. ? a. [3 , a. a. ? a. a. a. , ? j3 a. j3 , a. a. ? - Hal f-Life 4 . 5X1 0 1 0 years 24 days 1 . 1 minut es 2 . 3X1 05 years 8 . 0X1 0 4 years 1 . 6X 103 years 3 . 8 days 3 . 0 minutes 27 minutes 2 sec ond s 20 minut es -4 1 . 5X1 0 second 1 . 3 minut es 22 years 5 . 0 d ays 1 40 days 4 . 2 minut es Stable Half-Life 7 . 1 X1 08 years 24 hours 4 3 . 2X1 0 y ears 22 years 1 9 days 2 1 minut es 1 1 days 3 . 9 sec onds 1 . 8X1 0- 3s ec ond 3 . 6 minut es -4 1 0 second 2 . 2 minutes 5X1 0-3second 4 . 8 minutes Stable Thorium Series Element Symbol Radiation Thorium 232Th a. Mesothorium I 228Ra ? Mesothorium II 22 8Ac ? Radiothorium 228Th a. Thorium X 224Ra a. Thoron 220Tn a. Thorium A I 2 1 6Po a. Thorium B 2 12Pb ? , a. I _ 2 1 6At Asta?ine a. Thorium c ~ 2 1 2Bi ? , a. Thorium C 1 2 1 2Po a. Th I . ?n C" 208Th ? Thor?um I 208Pb or?um - ( end produc t ) Fig . I I I - 1 238 235 232 Decay S c hemes for U , U , Th Hal f-Life 1 0 1 . 4X1 0 y ears 6 . 7 y ears 6 . 1 hours 1 . 9 years 3 . 6 days 51+ sec onds 0. 1 6 sec ond 1 0 hours -4 3X1 0 sec ond 60 minutes 3X1 0-7sec ond 3 . 1 minutes Stable 75 . ft . . d th R 226 t . .. t a er a li ttla more th?n one m1ll1on years oes e a ac 1v1 y reach 97% of i ts equilibrium value . ( b ) There may h ?vc ? ecn s ome preferenti ?l loss ( e . g . by l eaching ) of one or more of the i s otopes in the dec?y series . I f radium has been los t preferenti:1l ly , a "percGnt r>.ge equilibrium rEJ.dium" value o f l ess th?n one hundred percent is to be expe c ted , whereas pre ferentinl loss of uranium will l ead to values of "per c entage equilibrium radium" greater thc:n one hundred percent . The mos t c omm0n method used to determine the "perc en tage equilibrium radium" reli es on the measurement o f the known trpes of radiation aris ing from the disintegration of uranium and i ts daughter pr?ducts . I t is necessary in this method to measure b o th beta and gamma radi ation . The beta radiation ?rises from both the immediate uranium daughter produc t s and also from radium . The major fraction of the gamma radi?tion ar?ses from radium and i ts daughters . The gamma radiation ?i gure is used to calculate the amount of beta radi?tion due to radium , and this is then dedu c ted from the to tal b e ta me?surement to determine the amount o f b e ta radi?ti on aris ing from the uranium . From this correc t ed figure , the amount o f urc.nium is determined .:::md the 0percentnge equil ibrium radium 1 1 c alculated . This i s essentially the method used by BOSIN and BOGDr,N ( 1 960 ) and STERN and STIEFF ( 1 959 ) . iLno ther approach is that of GR&CE and BATES ( 1 959 ) who det ermined the equil ibrium using alpha and fiss ion- fragment radiography . Thi s technique has the advantage that i t can be appl i ed on a micro s cal e but suffers from the disadvantage that it can no t be used in the presence of natural thorium . 76 . The main weakness in th? me thod involving the measurement of both beta and gamma radiat i on is the assumption that nll the gamma radiation detec ted is due to the decay of radium or i ts daugh ters . This is not s o , as Th234 and u235 both produce gQmma radiation , ?nd although the activi ty is only a frac tion of that from radium and i ts Gaughters , i t is s t ill s ignificant . As a result o f this , the correc ted beta figure for uranium would be too low , ::1.nd therefore the asso ciated ; 'perc entage equilibrium radium ' ' , value would be rather too high . The advantage offered by a method whi ch independently measures the radiation from only 226 235 Ra and a uranium iso tope is c learly seen ( U i s the mos t sui table uranium i so tope for a gamma ray s tudy as the decay o f U238 t P 234 d . ? . . d u234 . o a ocs not 1nvolve gamma em1ss1on an 1s insuffi c ien tly abundan t ) . LEDERER ( 1 969 ) s tates that the principal g?rnma rays from bo th u235 and Ra226 fi ?ve an energy o f 1 85 KeV and the princ ipal g?mma rays from Pb2 1 4 ( a daught er of Ra226 always i n equilibrium , due to i t s short half- l i fe ) have energi es o f 242 , 295 and 352 KeV respec tively . From these gamma rays i t i s thc:oreti cally possible . to calculat e t h e 1 1 percen tage equilibrium radium 1 1 ? To n chi eve this exp erimentally , however , i t i s nec essary 2 1 4 t o resolve the three Pb gamma rays , and to determine the extent to which the Ra22? 1 85 KeV gamma ray interferes wi th the 1 85 KeV gamma ray from u23 5 . Prior to the devel opment o f the Ge ( Li ) detec tor , the Pb2 1 4 gamma rays could no t be s::J..t i s factorily resolved , as the Nai ( Tl ) d e te ctor di d no t possess suffi c i ent resolution in this energy region . Fig . III-2 clearly illustrat es this point . ,:,1 though the Ge ( L i ) detector was developed primarily for the Cl) c c ea ? (.) .... Cl) a. en .... c ::s 0 (.) If c I I \ 210 Pb 100 >I ., ... ? ? aJ '6 I I f ? 1 1 ? 300 C ha nne l 235 2 26 U + R a 1 8 5 500 N u mbe r 2 1 4 Pb 2 4 2 700 Fig . I I I - 2 Comparison of uraninite spectra recorded with Nai (Tl ) and Ge (Li ) detectors 214 Pb 2 95 2 1 4 P b 3 5 2 900 Nal (TI ) K eV Ge ( Li ) 77 . b enefi t o f the nuclear spectros c opis t , i t h?s b e en used in many o ther fi elds o f research. These include decay- s cheme s tudi es w i th radioactive iso topes , b eam spec tr?s copy , low- t emperature nuc lear ori entation and a c t ivation analysis . An E xc ellent review o f the impac t o f s emic?nductor d e t e c tors on gamma-ray and elec tron sp e c troscopy i s given by HOLLANDER ( 1 966 ) . The preparation , maint enance ?nd relevant theory of the s emiconductor det e c tor i s given by Mr,NN ?T ;,1 ( 1 966 ) , DZ:;,RN"LY and NORTHROP ( 1 966 ) and CQ?:}TE ( 1 967 ) . The geochemist and analytical chemist h?ve gained mos t benefit from the Ge (Li ) detec tor i n the fi eld o f ac tivation analysis b ecause the high resolution obtained has , in m?ny c ases , made possible the dire c t measurement o f the irradiated s ample . Previously , using th? Nai ( Tl ) detec tor , t ? dious chemi cal s eparat ions were required . To the author ' s knowledge , the only ?ppli cati on of the Ge ( Li ) detec tor to naturally- oc curring radio? active material , is that of M?THEVON ET AL ( 1 967 ) , who used the gamm? radiat i ?n o f spe c i fi c i so top es to determine uranium , thorium and radium c ontent o f such samples . The method used by these authors required that the sample w as in radioactive equilibrium and that ?n ac curately known uranium s tandar d , also in equilibrium , was av?ilable as r e: ference . l'LTHEVON ?T !cL also developed a method t o compare the radioactive equilibrium of each sample with that of the s t3ndard rock . How ever , due to an error in the ass ignment of the 1 85 K eV gamma radi ?ti on by the above authors , the pres ent au thor cnnsi ders that the reported work i s in s erious error and r equires further elucidation . The aim o f this part o f the thesis was three- fol d : 78 . ( 1 ) To i dent i fy the various peaks in the low energy regi?n o f the gnmm? spec trum ( 30-360 K e V ) of naturally a c currin5 urnnium ores . ( 2 ) From the results o f ( 1 ) , to develop a me thod for determining the 1 1p ercentage e quilibrium radium" . ( 3 ) To invest igat e tha equilibrium s tate o f uranium minorals i n t h e Buller Gorge in order to provide more i nformation on the his tory of these depos its . 79 . INSTRUMENTATION ?ll ma?suremants were obtained vi? a high- resolution g?mma spe c trometer at the Inst i tute of Nuclear S c i ences , Department o f S c i enti fi c and I ndustrial Research , Wellington . High resolution in the l ow- energy region ( 40-360 KeV) was ob tained by using a 5 cm3 Ge ( L i ) d e t e c tor , dri fted from five s ides nnd w i th the open end fac ing the radiation . In a germanium d ete ctor only 3eV is required to produce an elec tron-hole pai r , whereas a Nai ( Tl ) crystal requires abou t 300 eV per pho to-ele c tron from the c athode and henc e has a much poorer resolution . Fig . I I I-2 c learly illus trates the d i fference in r esolution o f these d e te ctors . The Ge ( Li ) detec tor was coupled t o a SIMTEC P- 1 1 , low-noise Field-Effect- transistor pre-ampli f i er ; the combination provided resolution o f 2 . 5 KeV . These two c omponents were housed in the radiation area thirty to forty feet from the control room . Coaxial cables from the pre- ampli fi er l ead to the c ontrol room , where the pulses w ere ampli fi ed by an ORTEC 4 1 0 transis tor main amplifier whi ch was ?onnec ted to an 'RCL 256- channel pulse-height analyser ( P . H . ? . ) . For very ac curate calibration work a KICKSORT 4096- channel pulse-height analyser was us ed . Data s tored i n the memory of e ither P . H . h . were recorded as a spe ctrum l isting via a typ ewri ter , for later manual plotting , o r were punched dir e c tly onto paper tape whi ch provided the i nput informat ion for computer? assisted analysi s . Figures -I II-3 and I II-4 show s chematic diagrams of the gamma spe c trome ter , and the sys t em used for c ?mputer? assisted analysis 0f gamma spe c tra , respe c t ively. / ? - r ays \ Th i n AI Ga mma Spect roscopy Field Effect Transistor Preampl if ier C opper rod at l i q . N 2 A I mount t he rma l r ad i a t i on ~ Spe c t rum L i s t i n g . . Ma in Ampl i f ie r \ L ong coa x i a l c ab le to contro l room . . . ? Typew r i t e r Fig . I I I - 3 Gamma spectroscopy - schemat ic diagram 0 Q;) 0 0 0 I I I I I J 0 Pulse He i g ht Ana lyse r , 256 C hanne l s Tape fo r C omputor A na l y s i s Pu n c h e d Paper Tape From P. H. A . ,!-.. -, .- :' :? . . '1 I C ompu t e r P rog r ams On Pape r Ta pe C ompute r - ass i sted Ana lys is- of G a m ma Ray S pect ra . - . . ' . ' ' . " ? ' . ... ... , . ' ' . . . ... I . . . . . . I . . . . . . . . . . . . I I I I I I I I I I I I I Paper Tape R eader P D P-8 D ig i t a I Compute r ?? ? . D? ? ? . . . . ? . . . . . . Te l e t y p e For I nput C o mmands A nd Prog ram L i st i n g /?.-7? P l ott e d Spec t r u m ? X - V R e c o rd e r Fig . I I I - 4 Computer-assisted analysis of gamma spectra ?? ? Fast Paper ""'Tape P u n c h 1 ? : .?. : .? : : . ? ou?tput Paper Tape To Be U s e d When Req u i re d 8o . Operation Proc edure Five to fi fteen grams ( dep ending on the activi ty ) o f powdered rock ( less than 80 mesh ) wcs placed i n a cylindri c al glnss phial ( 5cm x 2cm diam . ) and posi tioned in front o f the detec tor next to the thin ?luminium window . The s?mplc was counted for a suffi c i ent time to allow a well-defined spec trum to be obt?ined . For most uranium minerals thi s was between fifteen and thiry minutes . ? check on the number o f c ounts per channel i n each channel comprising th e spe c trum was easily obtained a t any time via an oscillos cope in the P . H . A . When a well-de fined spec trum had been obtained , the number i n each channel was e i ther listed by the typ ewri t er or punched on to pap er tape and then analysed wi th the computer as h?s b e en previously describe d . A typi cal sp e c trum 0b tained i s shown i n Fig . I I I- 2 . IDENTIFICATION OF SPECTRA ( a ) Calibration o f Puls e Height tnalyser As has been previously menti oned , the gamma spec trum is r e corded by the P . H . ? . cs counts in ? given time for each channel . I n order to assign sp e c i fi c ener?i es to each p eak a calibration curve o f energy as a function c f channel number mus t be determined . The calibrati on curve was c ons truc ted from the gamma sp e c trum o f a s t ?ndard source , consis ting o f s everal i s o topes , by plot t ing the known energi es of the gamm3 rays frpm these iso topes ?gains t their corresponding channel numbers . Tabl e III- 1 shows s ome o f the i sotopes used , w i th their respe c tive gamma ray energi es , and Fig . I II-5 shows a typ i cal cal ibration curve obtained . Provi ded that the s e t tings on the spe c trome ter are kept c0ns tant , the calibration curve can be used for all spectra taken over several hours . I f , however , ?n ass ignment of an energy to a peak i s doub tful the cal ibration curve i s redetermined ei ther immediately b e fore or after the parti cular sp ec trum being s tudie d . ( b ) ?nalys is of Spec tra The analysis of the low- energy gamma ray region ( 30- 400 KeV) was carried out in two parts . The firs t , and mos t impor tant to thi s work , was a qu?li tative and quanti tative s tudy confined t o the region 1 80- 360 KeV . This region includes the main gamma radiation from u235 and Ra226 ( 1 85 KeV ) and the main gamma radiation from 2 1 4 Pb ( 2 42 , 295 , and 352 K eV ) . These are the most important gamma radir:ctions for the calcul?tion o f radioactive equilibrium . The s e cond part was c oncerned only wi th ident ifi cation of the observed peaks in the region 30- 1 80 KeV. The energy region above 360 KeV was not c ons i dered because it contains only gamma rays f B . 2 1 4 . f th rom 1 and y 1 elds no n ew in formation . Use of one o ese > Q) 280 240 200 ? 160 20 Fig . III - 5 40 60 80 100 1 20 Channe l 140 160 Numbe r Calibration curve , keV as a function of channel number 180 200 220 240 260 T1-.BLE III - 1 Iso top es and Respec tive Gamma Ray Energi es Used for Calibration of ? Pulse Height AnRlys er Iso topes Energi es ( KeV ) Ba1 33 30 . 9 , 8 1 . 1 ' 276 . 5 , 303 . 0 , 356 . 3 , Ra226 1 85 . 7 , 241 . 9 , 295 . 2 , 352 . 0 it m 2lt 1 26 . 35 , 59 . 54 Co57 1 2 1 . 97 , 1 36 . 33 Co6o 1 1 73 . 2 , 1 332 . 4 Pb2 1 0 46 . 5 82 . 384 . 1 gamma rays as a det ermination o f Ra226 was no t attempted b e cause of the very low d?tec tnr effic i ency in this energy range . hlthough no apprec iabl e amounts o f the thorium s eries were dete ct ed in the urani?m minE rals from the Huller Gorge ( a s i tuation whi ch reduced the complexi ty of the spec trum ) , the quantitative study carried out included the possibili ty o f the presence o f thorium in o rder 'V?, to ensure th?t this method of calculating radio?ctive equilibrium had general appli cation . ( i ) 1 80-360 KeV Region Fig . I II-6 shows ( i ) t?e gamma spe c tra obtained from a uranium mineral ( uranini tc ) , ( i i ) and Bi2 1 4 , ( i i i ) "uraninite minus R 226 . ' l ' b . "' J.' th Pb2 1 4 a J.n equJ. 1 r1um Ra226 :' and ( iv ) an aged thorium nitrate sample . The spectrum labell ed "uraninite minus Ra226 1 1 was obtained by counting the uranini te for two hours and sub- trac ting the c ounts obtained from the radium s ourc e over the s am e t im c . T o normalize the two count rates , the position o f the radium s ourc e . in front of the dete c tor was altered until the "perc entage l ive time" meter regi s tered the same value .:ts when the uranini t e sample was count e d . Thi s approach was consi dered to be the mos t suitable way to determine the extent o f interference o f the Pb2 1 4 peaks i n natural samples , aris ing from u235 o r o ther decay p roduc ts . I t i s es tim?ted that the error incurred by this procedure would not be greater than one p ercent . From F ig . I II-6 i t i s clearly s e en that the 1 85 K eV gamma 226 ray from Ra canno t be distinguished from the 1 85 KeV gamm? ray from u235 , and that the 239 KeV gamma ray from Pb2 1 2 ( a daughter o f Th232 ) interferes s trongly w i th the 242 KeV gamma ray from Pb2 1 4 A s a result o f a systematic s earch through TABLE OF ISOTOPES N 1 0 Cl) c: c: Ill ? u ... Cl) Q. 1/) - c: :I 0 (.) 6 5 4 3 2 0 3 2 0 235 226 U ? Ra 185 120 Fig . Ill - 6 214 Pb 214 Pb 295 352 352 U r a n i n i t e R a d i u m 226 " Uran i n i t e - R Thor i u m N i t ra t e 160 Chann e l 200 Numbe r 240 Gamma spectra of uranini te , Ra 226 , Th 232 ( Energies of peaks in keV ) . 84 . ( LED?RER , 1 969 ) these interferences were exp e c t e d but their respe c t ive quanti tative contr ibutions were unknown . The "uranini te ? R 226 ? r t h k t 350 7 K V m1nus a ' spec rum s ows a p ea a ? e ? 'I'his i s b bl d t o Bl.. 2 1 1 , d ht f u235 B . 2 1 1 . th 1 pro a y ue a aug er o , as 1 1 s e on y isotope present which has a . favourable decay path to produce a gamma ray o f this energy. Hence there i s interference of the Pb2 1 4 352 KeV peak by the B i2 1 1 350 . 7 KeV peak . Thi s B i2 1 1 interference prevents the Pb2 1 4 352 KeV peak from b eing use d as a measure o f Ra226 pres ent in the sample b e cause the B i2 1 1 2 1 4 contribution to t h e Pb p eak w i ll vary a c cording to the amount of u235 present in the sample . Further c onfirmation that the Pb2 1 4 352 KeV peak i s contaminated i s shown by comparing the ratio - 352 KeV peak/295 K eV peak from the uraninite wi th the 226 same ratio from the Ra spectrum . The values o f thi s ratio are 1 . 31 9 and 1 . 257 respect ively , which shows that the value of the 352 KeV peak from the uranini te is higher than would be expected if it was free from interferenc e . The spec trum ob tained ' from the aged thorium ni trate sample shows a s trong peak due to Pb2 1 2 at 239 KeV . h S the resolution of the sys t em used i s 2 1 2 2 . 5 Kev ; i t i s seen that the P b 239 KeV peak will interfere with the Pb2 1 4 242 K eV p enk and render i t unsui table as a measure for Ra226 ? These results show that 6nly the Pb2 1 4 2 95 KeV p eak is free from interferenc e , and i s suitable for use as ? measure f R 226 t ? . t o a ac 1v1. y . ( i i ) 30- 1 80 KeV Fegion The i denti fi cation of peaks from uranium sampl es in this energy range of the spec trum was att empted as l i t t l e information is available i n the li terature ? Preliminary exp eriments , w i th dissolved uranihi t e as s ?mple , were carri ed out to investigate the sui tabi l i ty of us ing solvent extrac tion t e chniques to s epar?te the various i sotopes nnd hence fac ili tate identi fi cation of their gamm? radiat ions . The sys tem chosen was tributyl phosphate/HCl as this was the best d<:> cumented ( s:.To , 1 966 ) . However , incompl ete s eparations w ere ob tained w i th this syst em . h successful s eparation was achi eved by using the anion- exchange t echnique reported in Part II of this thesis for the s eparation of uranium and thorium . Fig . I I I-7 shows the spec tra obtained . The exc ellent s eparation of uranium from thorium assisted i dent i fi cation of u235 gamma radiation and Th234 gamma radiation in this e nergy region . The spe c trum of the uranium frac tion shows that u235 emi ts the following gamma radiation and X-rays in the 30- 1 80 KeV region : 49 , 68 , 85 , 93 , 98 , 1 1 0 , 1 43 , 1 63 KeV . The spe c trum of the thorium fraction shows tw:. peaks due to the 63 KeV and 93 KeV gamma rays from Th234 . The u235 sp ec trum obtained in this work comp.'lres well w i th that obtained by MilNN ET i\.1 ( 1 966 ) ' .::J.lso using a G e ( Li ) detec t ,Jr , from a u235 source of 93% purity . The ur::::.n in i t e spec trum (Fig . I II-2 s!J.ows two p eaks at 76 and 89 KeV whi ch are absent from the uranyl ni trate S)..:: c trum . These peaks are Bi K x-rays , following the decay o f Pb2 1 4 ? Their absence 2 1 4 from the uranyl ni trate spe ctrum i s due t o the abs ence o f P b , b e cause o f the young age o f the sample . Similarly , a peak at 2 1 0 46 . 5 KeV , due t o P b , appears i n tha uranini te spec trum , but not in that o f the uranyl ni trate . The above resul ts show that this low- energy region ( 30- 1 80 KeV) i s extremely complex . The features with the b e s t C"' ' a 0 Q) c c RI 1 0 .s= () ... 8 Q) a. 6 !/) -c ::I 4 0 () 2 0 Fig . I l l - 7 234 Th 63 235 u 96 2 ,., t! X 235 u 1 10 235 u 1 85 Uranyl N i t rate U ran ium F ra c t ion 135 :.:: u 48 50 234 Th 93 143 Thor i um Fr act ion 100 150 Channe l N umber 200 Gamma spectra of uranyl nitrate , extracted uranium fraction and thorium fraction ( Energies of peaks in keV ) . 86 . possibilities for us e ful applic ?tions are the 63 KeV gamma radiation from Th234 ( as an indication o f u238 ) , and the 46 . 5 K eV gamma . 2 1 0 radiation ( as a measure of Pb . ? ) . However , the higher energy end ( 1 80- 360 KeV) of this low energy region appears to contain the most s ignifi cant informati on . EQUILIBRIUi"' STUDIES ON MINERALS ( a ) Derivation o f the Equilibrium Rel?tionship J:.s h:ts been previously menti oned , the term ' 'perc entage equilibrium ra.dium ; ' is the a c c epted way of expressing "the s tate o f equilibrium o f a uranium mineral . This term is defined as the amount of radium ac tually pres ent in the sample , expressed as a perc ant?ge o f the amount o f radium which would b e pres ent i f the sample was of suffi c i ent age to have attained a st?te o f equilibrium b etween the uranium and the products o f i t s decay . From the previous resul ts i t i s s een that i t i s possible to de termine the numb er of radium atoms present from the count rate obtained from ?he Pb2 1 4 295 K?V peak . The number of c ounts in uni t time at an energy of 295 KeV , C ( 295 ) , i s given by where APb ' NPb are the decay c onstant and number of atoms respec tively , of Pb2 1 4 , PPb ( 295 ) is the frac tion of disintegr?tions f Pb2 1 4 . . E ( ) ? rom g1v1ng a gamma ray of 295 KeV , and 295 1s the G e ( Li ) d e t e ctor effi c i ency at this energy . When Ra226 is in radioactive equilibrium with Pb2 1 4 , A N - A N Pb Pb - Ra Ra where ARa ' NRa are the decay constant and number of atoms respec tively , o f Ra226 ? This equilibrium is ?ttained i n a Ra226 sample after only a few weeks have elapsed . Hence the number of radium atoms in the sample is given by C ( 295 ) However , the absolute 9alue of the detec tor effi c i ency , whi ch i s 88 . di fficult to obtain w i th b e t ter thRn ten perc ent ?c curacy , mus t be dt:tcrmined experimentally for each detector used . ; _ s 3. resul t , this appro?ch is c ?nsider e d unsatisfac tory . To overcome this problem nn attempt was made ta ob tain a relationship b e tween the "percentnge equi l ibrium rc!.dium; ' .:md the rati o of the 1 85 KeV ( u235 + Ra226 ) peak to the 295 K?V (Pb2 1 4 ) peak in which the d 2 t e c tor effic iency term is no t involved . The following shows how this relationship was develop e d . L e t C ( 1 85 ) b e the numb er b f counts i n uni t time a t an energy o f 1 85 KcV , and l e t the det e ctor e ffi c i ency at this energy b e E ( 1 85 ) . Then C ( 295 ) and - - - ( 1 ) - -- ( 2 ) where A.U ' NU are the clec3.y cons tant ,J.nd number o f 3.toms , respec tively , o f u235 , PRa ( 1 85 ) , PU ( 1 85 ) are the fract i ons o f the disintegrations from Ra226 , u235 giving n gamma ray of the s tated energy . L e t A PPb ( 295 ) E ( 295) = Ra A PRn ( 1 85 E( 1 85 ) = Ra A uPu ( 1 85 ) E ( 1 85 ) = then C ( 295 ) = k1 NRa C ( 1 85 ) = k2NRa + k3NU NRa = C ( 295 ) /k1 and NU = ? iC( 1 85 ) 3 k1 k2 k3 hence Nu k 1 C ( 1 85 ) - k2 C ( 295 ) NRa = k7C(295) ;; = !szck1 k3 k2 C ( 1 85 ) - 1 ) . C(295 ) --- ( 3 ) ( 4 ) ( 5 ) -? -- --------------------- - !2 ( k1 ) - k3 k2 X - 1 C ( 1 85 ) where x = C(295 ) . / - - - ( 6 ) Now P involves the reL;.tive effi c iency o f the det e c tor K2 at 1 85 and 295 KeV , and mus t b e det?rmined experimentally by 226 me2suring xRa ' the value of x for the spec trum of pure Ra in equilibrium w i th i ts daughters . In this cas e , NU = 0 and henca X - !2_ Rn - k 1 ( 7 ) Thus ( 6 ) becomes ( !!Z From 3 ) , k = 3 ? - ? NRa - k3 A. RaPRa ( 1 85 ) X upu( 185 ) (? - 1 ) xRa 4 ? 32 . 1 0- 4 . 4 = 9 ? 7 5 . 1 0- !0. 54= 4 3 . 29 . 1 0 ( 8 ) where PRa ( 1 85 ) and PU ( 1 85 ) are obtained from LEDERER ( 1 96 9 ) . - 1 ) - - - ( 9 ) 238 - 226 When radioactive equilibrium exi s ts b e tween U and Ra , where A. U 1 ' NU 1 ' are the decay c ons tant and numb er o f atoms respe c tively , o f u238 ? But = 0 . 7 1 99 . 28 4 ? 32 . 1 0- 4 0 ?? 1 = 1 ? 53 . 1 0-10 . 99 ? 28 = and the value o f x for a sample in equilibrium , x8 , from ( 9 ) i s given by 90. Consi der . a s3mple c ont?ining NU atoms ?f u 235 . I f the sample were in radioactive equilibrium , ( N ) = Ra eq Nu 3 ? 29 . 1 04c xe _ 1 ) xRn In general , however , NR w ill b e a Henc e the p ercen tage equi l ibrium radium , R , i s = 0 . 6 1 . 1 00% --- ( 1 1 ) For the spec trometer sys tem used in the pres ent work the value o f xRa was found to b e 0 ? 607 (Fig .r III-6 ) . I t may be noted that the relative d e t e c tor effi c i ency can now b e calculated , that is E ( 1 85 ) E(295) = = 2 . 86 Subst i tut ion of the value xR = 0 . 607 i n equation ( 1 0 ) gives a Xe = 0 . 98 Thi s allows a graph to b e drawn giving p ercentage equilibrium radium , R , as a func tion o f x , using ( 1 1 ) . Thi s i s shown i n Fig . I I I-8 . From this graph , R can b e determined d irec tly from the experimental count-rates C ( 1 85 ) and C ( 295 ) . The appropriate value of xR for any o ther Ge ( L i ) d e t e c tor can be found by 1 a ? th t . C ( 1 85 ) R 226 measurlng e ra lO C(295) for a pure a sour c e . 11')1 11') CO 0.. ? N u u 2 ? 2 2 ? 0 1 ? 8 1 ? 6 1 1 ? 1 ? 4 >< 1 ? 2 1 ?0 0 ? 8 ----;:;-----:;;-????????=:::L::::. 20 30 40 70 80 1 20 1 40 1 50 100 1 1 0 1 30 50 60 90 Fig . I I I - 8 R % Theoret ical curve of C ( l B S ) as a function of the percentage equilibrium radium C ( 295 ) ( b ) The Isotopic Composition o f Uranium Minerals from the Lower Buller Gorge 91 . The gamrna spec tra o f thr.? e uranium s tande.rds and various primary and s e condary miherals , s elected from both the North and South Side deposits wore obtained , and their respec tive C ( 295 )/C ( 1 85 ) ratios were measured . From this ratio the i lperc entage equilibrium rnclium" , R , was calculat ed . T9.bl e I II-2 shows the values obtained . As has been previously mentioned , the mineralogy o f the uranium deposits has been thoroughly investigated and has been shown to cons is t meinly o f co ffini te on the North Side and ure.nini t o on the South Side , w i th b o th s ides c ontaining the s e condary minerals , gummi te , t0 rberni te , autuni tc and ur.'lnophane . However , b e cause o f the physi c ?l d i f ferences obs erved among many o f the 1 1uranini t e " samples measured , i t wo..s considered necessary to i nves tigate their mineral form . For example , the so..mples labelled 4 and 5 i n Table I I I-2 wer e in fact obtained from the same rock , the top half o f whi ch was black and the b o t tom hal f bright yellow . An.'llysis o f each frac t ion gave 1 7 . 5 and 1 6 . 0 perc ent uranium resp ectively . The corresponding values o f R show that the black frac tion is nearer to equilibrium than i s the yellow frac tion . M ineral i denti fi cation was effected by the use o f an X-ray powder d i f fractome ter . The samples s tudied had previously b e en s eparated into three dens i ty frac tions by use o f bromo form , methylene iodide and cleri c i solution . The frac tion o f the original sampl e whi ch h?d a dens i ty greater than c l eri c i solution was used for the powder mount . The i denti fi cati ons ob tnined are given i n Tabl e III-2 . From this table i t is s e 0n that none o f the uranium T;,BLB I I I - 2 The Equilibrium S tnte o f Various Uranium Minerals from the Lower Bull8r Gorge Su.mple I No . Mineral Form 1 85 295 1 13 - uo2 3 . 1 4 3 . 00 2 !3 - uo2 6 . 75 5 . 50 3 13 - uo2 1 1 . 60 1 1 . 30 4 13 - uo2 1 3 . 1 0 1 2 . 90 5 I .:mthini te uo2 . 5uo3 . 1 oH2o 8 . 30 7 . 55 6 Co ffini te 8 . 40 7 . 1 0 7 Coffinit e 1 0 . 30 8 . 48 8 Torberni t e * 7 . 80 6 . 90 9 U03 " 2H20 4 . 80 4 . 78 1 0 1\.u tuni t e * 4 . 83 2 . 80 1 85/295 1 . 045 1 . 225 1 . 030 1 . 02 1 . 1 70 1 . 1 85 1 . 2 1 5 1 . 1 30 1 . 050 1 . 725 Samples 1-5 and 9 taken from T-J hori zon ( Se e Fig . I I- 1 0 ) . Snmples 6 and 7 taken from North S i de . Samples 8 and 1 0 taken from S-C horizon . * Identified visually. 92 . R% 83 59 85 86 65 64 6 1 70 83 33 93 . minerals taken are in equilibrium . This is not unexpe c ted , as petrologi cal s tudies by WHITTLZ ( 1 960 ) showed that i n many cases the uranium minerals were al tered due to weathering proc esses . The f::tc t thnt the value o f R is l oss th.:m one hundred perc ent means that e i ther radium has baen lost from the sample or the sample i s . l ess than one million ye'lrs old , the time t?ken to attain equil ibrium . WILLI.'\MS ( 1 957 ) quo tes nn age determination of tha Rio Tinto Company on a sample of c offini te from the North Bank as lying wi thin the rnnge of one hundred million to one hundred and fi f ty million years . This indi cates a Cretac eous age for the mineral i zation . Approximate age determin ::tti ons were ob tained for a sele c tion of uranini te samples , from the South S i ce , by using the Pb206;u238 method ( KULP ET f,L , 1 954 ; ECKELM1?NN and KULP , 1 957 ) and by making t?e following assumptions : ( 1 ) The total uranium measured was t?ken to b e u238 . ( 2 ) The to tal l ead measured , l ess an es timated b?ckground value , The background vqlue w2s obtained by analysing l ead in a non-radioac tive por tion of the matrix materials . W i th these assumptions the ages of four uranini te samples were calculated to be 77 , 97 , 1 30 ?nd 1 80 million years . These values , supported by the value ob.tained for the North Bank c offini t e , indicate qui te c learly that the minerali zation is of the order o f one hundred million years old and therefore the "percentage equilibrium radium" values of l ess than one hundred p erc ent must be due to preferential loss of rqdium . I t i s usually assumed that uranium is leached preferentially to radium b ecaus e of i ts greater solub i l i ty . However , i f this s equence held for the samples s tudied , the vnlue 0f the 1 1perc ent <:>.:;e equilibrium r.:d.ium" obtained would b e 94 . greater than one hundred p orc cnt . Therefore i t is c oncluded by the ?u thor that preferential leaching of radium has taken place . This c onclusion is supported by the resul ts ob tained from two separate experiments carri ed out by SThRIK ET AL ( 1 95 1 ) to inves t ignt? the relat ive d iffi cul ty of l eaching of uranium and radium from uranini te . These authors showed that when uranini t e was l eached w i th d?st illed water , or w i th various c oncentrations of ni tri c ac i d , or w i th sodium carbonate solutions , the radium was l eached pre ferenti ally w i th respect to uranium in all cases . The s e cond experiment involved the analysi s for uranium and radium o f the outer- surfac e , mi ddle-portion and c entral core o f ? b o th intact and deformed uranini te sampl es . The intac t samples showed no di fferences but the deformed samples showed that radium had been preferenti ally removed w i th respe c t to uranium . hs WHITTLE has shown that the uranini te s?mples are slightly w eathered , the author ' s expl?nation of the values of the "p erc entage equilibrium radium" obtained for these samples appears consistent . Tabl e III-2 also shows that uranium samples in whi ch the uranium exists as U ( VI ) are of ten further from equilibrium than those samples in whi ch the uranium exis ts as U ( IV ) . The low values o f ' ' perc entage equilibrium radium ' ' obtained for such samples , may be due to continuous l eaching or as a result of insuffi c i ent time to attain equilibrium since the ini t ial depos i tion of the uranium from i ts original primary mineral . Because o f the c omplexity of this s i tuation , i t i s C8nsi dered by the author , that equilibrium s tudies on s econdary uranium minerals provide l i t tle information conc erning the history o f these minerals . This is no t so w i th primary miner?ls where a knowledge o f this equilibrium i s most informative . 9 5 . DISCUSSION The results pres ented in Par t I I I of thi s the s i s cl early show that the development of the repor ted t e chnique for the d e termination of the 1 1?wrc ento.ge equilibrium radium " was :tJrim <.:trily dependent on the eluc idati on of the low- energy gamma ray sp e c trum . The successful i dent i fi c?tion o f most peaks was obtained as a result o f effici ent chemi c?l s eparati ons , which reduced the number of int erferences from the various iso topes pres ent , ac curo. te pulse-height analys er calibrations , judic i ous use o f s tandard sources and care ful , syst emati c evaluation o f the data o f 2 1 4 LEDERER ( 1 969 ) , Thes e results showed that the Pb 295 KeV gamma ray was the most sui table to measure , . d . t " . f R 226 as an ln 1 c a lOll o a ? ? as i t was free from interferenc e . Thi s made i t possible to derive the relationship b e tween the 1 85 KeV peak ( u235 and Ra226 ) and 295 KeV peak in t erms of the "percentage equilibrium radium" . Thi s method will b e referred t o in future as the "Dire c t Gamma Hethod 1 1 ( D . G . M . ) . The advantages of this m e thod over previous methods are thr e e fold . Firs tly , and most important , only radiation from s p e c i f i c i s o topes is measured whereas i n previous proc edures , the total beta and total gammn radiation of all i s o topes pres ent i s measured . S e condly , the derivation o f the equilibrium relationship shows tho.t the 1 1D . G . H . 1 1 is independent of detec tor effi c i ency and as such is su,erior to the previous methods whi ch require thi s to be accurat ely known , a determination whi ch i s d iffi cult t o obtain . Thi rdly , the "D . G . M . " i s s impl e to us e and requires , depending on the ac tivi ty o f the sample , only fi fteen to thirty minu tes counting t ime . The main disadvo.ntage is that it requires a Ge ( L i ) det e c tor , high resolution pro-ampl i f i er and r easonably sophisti cated 96 . ?lec truni c s . The use of the nn . G . M . 1 7 for determining the nperc ent ".!ge equilibrium radium ' ' of uranium ores from the Buller Gorge showed th?t i n no ins t ?nc e were any of them in radio?ctive equ ilibrium . The s i gni ficGnce o f this has been d is cussed and apart from re? emphas ing that the mineral i zation appears t o be o f Cr?tac eous age nnd has undergone slight weathering , will not be discussed further , as the origin and his tory o f the minerali zation i s outs i de the s cope of this thes i s . I t is importan t to add that the "D . G . M . " can nlso be applied for the quantitative det srmination o f uranium . This simply involves obtaining n spec trum of the ur?nium sampl e , measurement of the 295 and 1 85 KeV peaks and the calculation of the ac tual number o f 1 85 KeV gamma rays from u235 as described earlier i n this s e c tion . A plo t o f the numb er o f counts per uni t t ime as a func t i on o f uranium content , obtained e i ther by chem i cal me thods or from s tandards , nllows a working curve to be constructed whi ch is appli cable to any uranium ore i rr espec tive o f i t s s tate of equilibrium . To summ?ris e , this part o f the thesi s reports on the i dentifi cation of gnmm? radiation in the low energy region of the spec trum , 30- 360 KeV for naturally- o c curring uranium minerals . To the author ' s knowledge , this is the firs t time that this has b een suc cessfully achi eved . Reported also , is the development nnd suc cessful use , of a new metho d for the determination o f "percentage equilibrium rndium11 , an important quanti ty in the s tudy of uranium mineral i zation . G'ENERAL DISCUSSION 97 . The aims o f this thesis , as mentioned in the General Introduc tion were threefold : ( 1 ) To develop" a me thod for the analysi s o f low conc entrations o f yttrium , thorium and rare e ?rths with the use o f a l arge quartz- opti c s s?ec trograph . ( 2 ) Tn inves tigate the possible ass oc iation of the above elements , and any other elem ents , w i th uranium in the minerals from the South Side o f the Buller River and to s tudy the dis tribution o f thes e elements in the weathering s equenc e : minerals , soils , s tream s ediments . From these results , to examine criti cally the relative merits of direct analysis of uranium and of asso c iated elements in s tr eam s ediments , as a geochemi cal prosp e c ting method for uranium minerali zation . ( 3 ) To develop a metho d , using only gamma radiation from u 235 and R 226 a , to d etermine the 1 1p ercentage equilibrium radium" of uranium minerals . The resul ts presented in Parts I , I I and I I I of this thesi s show that the above aims have lareely been achi eved . The analyt i cal s e ction in Part I showed that , by careful s elec tion of conditions , together wi th an e ffi c i ent s eparation s cheme , a large quartz-opt i c s emission spectrograph could b e successfully used t o analyse low conc entrations of yttrium , thorium and rare earths . The results obtained for the standard ro cks G- 1 and W- 1 subs tanti ated this claim and indicat ed the ac curacy that can be ob tained . Fresh data for the ?bove elements in C?hS s yenite were also provided and these agreed well wi th the results o f TENiL ?NT and FELLOWS ( 1 967 ) anc? CHii.HP ( 1 96 8 ) , the only other results ob tained for thes e e l ements in this s tandard rock . The main dis- 98 . advanta3e of the reported technique i s that i t is not readily appli cabl e as a rautin8 method for the rnpid analysis o f yttrium , thorium and rare earths in geologi cal sampl es . This is due to the l imi tation of the dissolution stage in the preparat i on of the sample for the ion-exch?nge column . The solution necessary to ensure separation on the resin , a mi xture of acetic ac i d and nitric acid , is an extremely poor solvent for geologi cal samples . However , i f the s eparation stage of the analytical procedure could be improved , this would then render the method qui t e suitable for rapid , routine analysi s . ?lthough the geochemi cal study i n Part I I showed no apparent associati on o f yttrium , thorium and the rare earths wi th uranium , the data were , nevertheless , important as they provi ded new evi dence for the possible origin of the Hawks Crag Brec c ia from the Paparoa Range . Copper , b eryllium and l ead di d , however , show good correlations at various stages down the weathering sequence ; o f these elements , copper showed the best c orrelati on in the s tream sediments . This s tudy showed that in this area o f high rainfall and rugged topography , the analysis o f c opper as a "pathfinder" for uranium app eared to be a b et ter indi cation o f the known mineral i zation than was the analysi s of uranium . Thi s was explained by the lower solub i l i ty of c opper c ompared w i th uranium . However , the use o f copper alone ns an indi cation of uranium mineral i zat ion was not c ?nsi dered comple tely reliable becaus e o f unrepresentative sampling and the presence o f di fferent amounts of unmineralized matrix material . This variati on in sampling 9 9 . o ften arose as a result o f a l ack o f f ine s ediment in the main flow of the streams . To overcome these twn problems , ratios of l ead , zinc and copper were taken in an at tempt t? minimise such fluctuat i ons . In general the results obtained from these r?ti os showed similar patterns t o those reflected by the analysi s o f copper alone . I t i s cons idered by the author , however , that al though the results appear promising , a more de tailed s tream- sediment sampling programme would need to be carri G d out b e fore this t echni que could be considered completely rel iabl e . ? i th regard to d irec t analysis o f uranium in s treGm sediments , this study d i d show tha t , except when samples w ere taken wi thin thirty to forty yards of a reasonably large , active outcrop of uranium mineral i zation , the analys is o f s tream s ediments for uranium gave no indi cation o f surrounding mineral i z?tion . In fac t , uranium anomali es in stream s ediments could only be detected over distances simi lar to those for whi ch radiome tric i nstruments were useful . I t i s consi dered that Part I I o f this thesis has clearly shown that , b ecause of climat i c or topographi cal d ifferences , t e chniques whi ch are used for geochemical ?respec ting o f uranium mineral i zation in o ther parts o f the world may not be invariably applicable in o ther areas . I t i s t o be expected that the pathfinder elements will also vary from one uranium depos i t to ano ther and i t is there fore always nec essary to carry out ? preliminary or i entation survey of each new area . From a knowl edge o f the geology of the qrea , e l ements l ikely to be associated w i th the mineral be ing sought can be cho sen . Part I I I o f thi s thesis i s l argely a s tudy o f the gamma L I BRARY l. J A CCCV 1 1 .. 1 1 \ /C nC' ITV 1 00 . ray sp ec tra o f uranium mineral s , and s hows the deve lopment of a new t .; chnique for the de t err.1ina t ion of "pcr c en t.:"tge equ i l i bri urn radium ' 1 ( i n this thes i s cF.J.llecJ. the 1 1Dir e c t G 'i.mmo. He tho ,J l ' ) , whi ch w i l l prov i d e geolo?i s t s w i th a use ful tool for the s tudy of the origin and h i s t ory of ur'lnium minerali zation . Oth er me thods are av?i labl e to d e t ermine the nperc entage equ i l ibrium radium" , but the "D . G . tvl . " ho.s two m :tin advcm t o.ges . Firs tly , it measures only rad i?tion aris ing from the i s o topes conc erned , whereas the previous me thods involve as sump ti ons concerning the o.s s i gnmcnt of radiation to the parent iso top e s . S e c ondly , the "D . G . N . n i s ind ep endent o f d e t e c tor e ff i c i ency and relies only on o. ra t i o of the numb er of counts obtained from the 1 85KeV and 295KeV gamma rays resp e c ti vely and n o t 0n the absolute det ermination of the number o f be tn and g;:,mma rc.di .".. t i ? ms emi t t e d . The 11 c curo.cy of the "D . G . M . 1 1 dep ends only on the ac curacy of the valu es for the de cay constants , ?Ra and ?W ' and on the a c curacy of the values determined for the r e sp ec tive gamma ray decay path PR3 ( 1 85 ) and P0 ( 1 85 ) . The ac curacy of the?e values i s cons i dered to be ? 2% , whi ch yi el ds ../cin error of + 5% i n the value for the "per c entage equi l ibrium radium ' i . The error due to coun t i ng s tat i s t i c s can be made almos t negl i gibl e by increasing the c o unting t ime . A t the present s tage of developmen t , the : 'D . G . M . " cnn be us ed to d e t erm ine the i 'p er c ent3.ge equi l ibrium radium 1 1 for minorals c ont;:cin ing 0 . 1 % u3o8 or grea t er w i th ?n accuracy of ? 5% . The r esults from age det erminati ons and the values obtained for the "perc entage equilibrium ro. c? ium" sugge s t ed , qui t e s trongly , th?t the uranium mineral i za tion has remained i n i ts original s i te 1 01 . of ?eposition over 2 period of approxim?t ely one hundred million years . These results do provide information c onc erning the h i s tory of the uranium but they do no? tell us anything about i ts origin . ?l though s ome consi deration of the origin was made in Part II , a fuller d iscussi on of thi s sub j ec t i s outside the scope of this thes i s . To summarise , this thesis has developed two analytical methods , one in the f ield of el emental analysi s nnd the o ther in the field of radiochemistry , whi ch should find applicat i ons in the fields of analytical chemis try , geochemistry and geology . The cri t i c al evaluation o f geochemical prospecting methods , dis cussed in this thesis , should provide the basis for the development o f such techniques for use in further uranium prosp e c ting in New Zealand . The author considers that future studies in the urani ferous , Buller Gorge region should be c arri ed out w i th the following aims : ( 1 ) To subs tantiat e further the val id i ty of the use o f copper as a pathfinder for uranium by a more detailed and comprehensive survey of the s treams draining thi s area . ( 2 ) T o t e s t the hypothesis that uranium was l eached from i ts origin in the grani t e of the Paparoa Range and redeposi ted i n the present s i te in the Hawks Crag Bre c c ia . Such a study would include the analysi s of the trace-el ement content of the grani t es from ?o th the Paparoa Range and Hawks Crag Breccia in con junc tion w i th p e trological investigati ons . 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