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Uranium and thorium concentrations in an estuary affected by phosphate fertilizer processing: Experimental results and a modelling study

Periáñez Rodríguez, Raúl; Martínez Aguirre, Aránzazu

Abstract

The Odiel river, in southwest Spain, forms an estuarine system which is affected by waste disposal from a fertilizer complex. Uranium and thorium concentrations in waters and suspended matter, activity ratios and distribution coefficients, kd, have been measured along the river during two different tidal states. The results have shown that a radioactive impact is being delivered to the river, as well as a significant variability depending on the sampling point and the tidal state. Thus, a quantitative study of the distribution of radio-nuclides can be carried out best by means of a mathematical model. The model includes the partition of radio tracers between four phases (water, suspended matter and two sediment fractions) and has been designed for non-equilibrium conditions. Thus, radiotracer transfers are described in terms of kinetic transfer coefficients instead of Kds. The model simultaneously solves the hydrodynamic equations, the suspended matter equation (including depostion and resuspension processes) and the equations which describe the time evolution of radionuclide concentrations in each one of the four phases. The model has yielded good results in predicting U and Th concentrations in water and suspended matter, distribution coefficients and mass ratios.

Full text

J. En i on. Radioac i i y, Vol. 35, No. 3, pp. 281-304, 1997 0 1997 Published by Else ie Science Limi ed All igh s ese ed. P in ed in I eland ELSEVIER PII: SO265-931X(96)00057-4 0265-931X/97 $17.00 + 0.00 U anium and Tho ium Concen a ions in an Es ua y A ec ed by Phospha e Fe ilize P ocessing: Expe imen al Resul s and a Modelling S udy R. Pe ihiiez & A. Ma inez-Agui e Dp o Fisica Aplicada, E.U. Ingenie ia Tkcnica Ag icola, Uni e sidad de Se illa, C a U e a km 1, 41014 Se illa, Spain (Recei ed 16 Feb ua y 1996; accep ed 25 June 1996) ABSTRACT The Odiel i e , in sou hwes Spain, o ms an es ua ine sys em which is uj ec ed by was e disposal om a e ilize complex. U anium and ho ium concen a ions in wa e s and suspended ma e , ac i i y a ios and dis ibu ion coe icien s, kd, ha e been measu ed along he i e du ing wo di e en idal s a es. The esul s ha e shown ha a adioac i e impac is being deli e ed o he i e , as well as a sign jiican a iabili y depending on he sampling poin and he idal s a e. Thus, a quan i a i e s udy o he dis ibu ion o adio- nuclides can be ca ied ou bes bq’ means o a ma hema ical model. The model includes he pa i ion o adio ace s be ween ou phases (wa e , suspended ma e and wo sedimen ac ions) and has been designed o non-equilib ium condi ions. Thus, adio ace ans e s a e desc ibed in e ms o kine ic ans e coe icien s ins ead o kds. The model simul aneously sol es he hyd odynamic equa ions, he suspended ma e equa ion (including depos ion and esuspension p ocesses) and he equa ions which desc ibe he ime e olu- ion o adionuclide concen a ions in each one o he ou phases. The model has yielded good esul s in p edic ing U and Th concen a ions in wa e and suspended ma e , dis ibu ion coe icien s and ThjU mass a ios. o 1997 Published by Else ie Science Limi ed. All igh s ese ed 1 INTRODUCTION The Odiel i e is loca ed in he sou hwes o Spain. A i s lowes eaches, i o ms a idal es ua ine sys em which discha ges in o he A lan ic Ocean. 281 282 R. Pe ici iez, A. Ma inez-Agui e The es ua y is close o a la ge indus ial a ea in which a phospha e e i- lize p ocessing complex ope a es. This complex p ocesses a ound 1.6 MT o phospha e ock pe yea om Mo occo, Senegal and Togo. Pa o he was e is eleased di ec ly in o he Odiel i e . I is well known (Van de Heijde e al., 1988; Laiche & Sco , 1991) ha such was es con ain signi ican amoun s o na u al adionuclides: U, Th, Ra and hei daugh e s. The p esence o 226Ra and 224Ra in wa e and suspended ma e samples collec ed om he Odiel i e has al eady been in es iga ed (Pe ia iez & Ga cia-Leon, 1993; Pe iaiiez e al., 1994a). These s udies ha e e ealed ha a adioac i e impac is being deli e ed o he i e since, o ins ance, le els up o 670mBq 1-l o 226Ra ha e been measu ed in a wa e sample collec ed close o he e ilize complex. Al hough he e a e da a on he U- and Th-iso ope con en in he Odiel i e wa e and suspended ma e (Ma inez-Agui e e al., 1994a), a mo e de ailed s udy is epo ed in his pape . The objec i e o his wo k is o unde s and he U and Th dispe sion mechanisms in dynamic aqua ic sys ems, including he dis ibu ion be ween he solid and liquid phases as well as he e ec o idal oscilla ions. Thus, wa e samples we e collec ed along he Odiel i e a wo di e en idal s a es (high and low wa e ) and he U- and Th-iso ope con en s in wa e and suspended ma e we e measu ed. The dis ibu ion coe icien s kd we e also calcula ed. A quali a i e desc ip ion o he esul s is no s aigh o wa d as he e is signi ican a iabili y in ac i i y concen a ions and kd, depending upon he sampling poin and he idal s a e. This is a logical esul since we a e dealing wi h an open sys em in which some di e en e ec s a e aking place a he same ime: non-cons an inpu om he sou ce, adso p ion o adionuclides on o suspended ma e and bo om sedimens, deso p ion, and wa e and suspended ma e mo e- men s due o ides. Thus, a quan i a i e unde s anding o he U and Th dispe sion can be achie ed bes by means o ma hema ical models. A wo-dimensional model, ha includes he ans e p ocesses be ween ou phases (wa e , suspended ma e and wo g ain size ac ions o bo om sedimen s), has been applied o he Odiel i e . The model simul- aneously sol es he hyd odynamic equa ions, he suspended ma e dynamic equa ion (including he esuspension and deposi ion p ocesses) and he equa ions ha desc ibe he ime e olu ion o adionuclide concen a ions in o each o he ou phases. Al hough he model has been p e iously applied o s udy he dispe sion o 226Ra in he Odiel i e (Pe iaiiez e al., 1996a), he e a e wo main objec i es in applying i o U and Th: o achie e a quan i a i e unde s anding o he expe imen al esul s and o p o ide ex a alida ion o he model, ha is, o alida e he model o elemen s wi h e y di e en geochemical beha iou s, such as U and Th. U anium and ho ium in an es ua y 283 In he nex sec ion, he sampling and expe imen al me hods a e desc i- bed. Nex , he expe imen al esul s a e discussed. The modelling wo k is desc ibed in Sec ion 4. 2 EXPERIMENTAL Wa e samples we e collec ed in plas ic bo les along he Odiel i e basin (see Fig. 1) du ing July 1990. Two samples we e collec ed om each sampling s a ion: one du ing high wa e and he o he du ing low wa e so as o s udy he in luence o idal oscilla ions on he esul s. The wa e was il e ed as soon as possible h ough p e iously weighed Nuclepo e il e s (0.4pm po e size) o sepa a e he suspended ma e . The il e was hen d ied and weighed o calcula e he mass o eco e ed ma e . Typical suspended ma e concen a ions in he Odiel i e anged om 24 o 50ppm, depending on he sampling poin and he idal s a e du ing sampling. The il e was hen co e ed wi h HCI and in oduced in o an ul asonic ba h o hal an hou , du ing which, he suspended ma e was sepa a ed om he il e and dissol ed. The il e was hen washed wi h Fig, 1. Map o he Odiel i e showing he sampling poin s. The ec angula box is he g id used in he model. 284 R. Pe ici iez, A. Ma inez-Agui e HNOs which was added o he HCI o o m aqua egia. This solu ion was slowly hea ed o dissol e all emaining pa icles. U anium-232 and 229Th spikes and Fe ca ie we e added o he il e ed wa e and o he solu ion ob ained a e he dissolu ion o suspended ma e pa icles. P ecipi a ion o Fe wi h oxyhyd oxides wi h concen a ed amonium hen ollowed. U anium- and Th-iso opes we e ex ac ed om he p ecipi a es by using anion exchange esins (DOWEX AGlX8, HCl o m) and elec opla ed on o s ainless s eel planche s. Ac i i ies we e measu ed wi h Si ion-implan ed de ec o alpha spec ome y. De ails o he adiochemical and measu e- men me hods can be ound in Ma inez-Agui e (1991). 3 EXPERIMENTAL RESULTS Wa e samples a e deno ed by ‘0’ and suspended ma e samples by ‘SO’. The numbe s gi en o each sample iden i y he sampling s a ions (see Fig. l), which a e dis ibu ed along he low eaches o he i e , close o he e ilize complex. S a ion 1 is, howe e , a ups eam o his a ea. As i is no belie ed o be a ec ed by idal oscilla ions, only one sample was collec ed he e. The esul s o low and high wa e suspended ma e samples a e p esen ed in Tables 1 and 2, espec i ely. In he case o he low wa e samples, he e is a high concen a ion peak a s a ion S04, o bo h U and Th, e ealing he p esence o a local sou ce o ac i i y. Up o 86 and 116 pg g- o U and Th, espec i ely, ha e been measu ed in his sample, alues which a e much highe han hose p e iously ound o suspended ma e samples collec ed om o he i e s. Indeed, U concen a ions anging om 1.8 o 2.4 pg gg’ ha e been de ec ed in he Amazon and Mississippi i e s (Moo e, 1967). On he o he hand, Th concen a ions in hese i e s ange om some 8 o lOpgg_’ (Moo e, 1967). In some Japa- nese i e s, Th concen a ions ange om some 2.2 o 6.7 pg g-’ (Miyake e al., 1973). Thus, i seems clea ha samples SO4 and S05, collec ed close o he e ilize complex, a e a ec ed by he was e disposal om he complex. In he case o he high wa e suspended ma e samples, he dis ibu ion o Th and U is di e en . The maximum Th concen a ion is 0.7pgg-‘, and he e is a gene al homogeniza ion o concen a ion le els. This could be due o idal mixing, inpu o non-con amina ed suspended ma e om he sea and a non-cons an inpu o con aminan s om he sou ce ( he e ilize complex). On he o he hand, U concen a ions a e also lowe han du ing low wa e , al hough he e is s ill an impo an peak in sample U anium and ho ium in an es ua y 285 TABLE 1 Concen a ions o U and Th (pgg-‘) o he Suspended Ma e Samples Collec ed Du ing Low Wa e , and Ac i i y Ra ios Sample U1 [Th/ 234 Ui23R U 230Th/232Th ThjU so1 l.lOz O.24 1.2 I 0.3 so2 1.08 0.13 0.07 I 0.04 1.27 0.14 7*4 0.06 i 0.04 so3 2.03 i 0.24 0.11 0.05 1.39z o.17 9 4 0.05 x 0.03 so4 86 I 10 116&6 0.98 0.05 5.28 z!z 0.13 1.35 0.17 so5 25.3 z 1.3 31 3 1 .OO 0.07 6.1 0.7 1.22z o.13 SO6 13.4 1.5 0.052 z 0.024 1.07 0.17 2.4 & 1.4 (3.9 + 1.8) x 1O-3 so7 19.1 I 1.7 1.06 z 0.06 E o s a e la. TABLE 2 Concen a ions o U and Th (pg g-‘) o he Suspended Ma e Samples Collec ed Du ing High Wa e , and Ac i i y Ra ios Sample so1 so2 so3 so4 so5 SO6 so7 l.lOz O.24 3.9 * 0.5 2.8 0.3 9.oz 1.0 69 i 3 1.6 IIZ 0.4 2.4 zk 0.4 F”hl 0.12 0.07 0.19 z 0.07 0.27 0.13 0.06 0.04 0.7 * 0.2 234u1238u 230Th/232Th ThjU 1.2zlco.3 1.12 0.16 13 8 0.031 0.018 1.09 0.10 3.2 1.4 0.07 * 0.03 1.24 0.10 1719 0.030 z 0.015 1.04 * 0.07 0.9 k 0.3 8 5 0.04 0.03 0.91 0.17 5.1 * 1.9 0.29 k 0.10 E o s a e la. S05, which is close o he e ilize complex. This e ec has al eady been obse ed o 226Ra (Pe ia iez e al., 1994a). In gene al, 234U/238U ac i i y a ios a e compa ible wi h he exis ence o secula equilib ium in samples in which high U concen a ions ha e been de ec ed. This is no a ypical ea u e o i e s, bu i is ypical o he mine als used o e ilize p oduc ion (Ma inez-Agui e e al., 1994a). The secula equilib ium ound sugges s an ex e nal o igin o he suspen- ded ma e pa icles, which mus be he e ilize complex. The 230Th/232Th ac i i y a ios a e highe han 1 all along he i e o bo h high and low wa e suspended ma e samples. This e eals he high con amina ion by membe s o he 238U adioac i e chain. The exis ence o an ex e nal sou ce o ac i i y is con i med om he Th/ U mass a ios. Since U is conside ably mo e soluble han Th, i is o en ound in de ici wi h espec o Th in he solid su ace en i onmen . Thus, suspended ma e in unpe u bed i e s usually has ThjU mass a ios 286 R. Pe i&ez, A. Ma inez-Agui e abo e 1. This is no he case wi h he Odiel i e . I can be seen, in Tables 1 and 2, ha , wi h he excep ion o samples SO4 and SO5 in low wa e , he Th/U mass a ios a e below 1. This con i ms he exis ence o an ex e nal sou ce o U con amina ed pa icles o he i e . The excep ions men ioned abo e show a ios abo e 1, alues which a e ypical o unpe - u bed i e s’ suspended pa icles (al hough hey a e he mos con ami- na ed samples). These esul s will be discussed u he , wi h he help o he ma hema ical model. The esul s o he wa e samples a e p esen ed in Table 3. Un o u- na ely, only he low wa e samples could be measu ed (due o echnical p oblems in he labo a o y). Sample 01 shows an anomalously high U concen a ion wi h espec o he es o he da a. The e y low pH o he wa e , 2.86 (Pe iaiiez & Ga cia-Leon, 1993) due o local geology condi- ions (Ma inez-Agui e e al., 1994b), accoun s o he enhanced U concen a ion. The acid wa e s a ound s a ion 1 p o oke a dissolu ion o U om he solid phase (suspended ma e and bo om sedimen s) o he liquid phase. This e ec has also been obse ed o Ra-iso opes (Pe iaiiez & Ga cia-Leon, 1993). The pH o wa e s downs eam om s a ion 01 anges om 6.3 o 7.6; hus, his e ec does no ake place (Pe iaiiez & Ga cia-Leon, 1993). High U concen a ions a e also obse ed all along he s udied a ea wi h a peak a ound sample 04, close o he complex. Indeed, U concen a ions in i e wa e ange om some 0.02 pgll’ in he Amazon i e (Be ine e al., 1970) o some 3.5 pgll’ in he Nahe i e (Mangini e al., 1979). Simila alues we e ound in some Indian i e s (Bha & K ishnaswamy, 1969). Thus, i seems ha an inpu o U- con amina ed wa e is aking place a ound he sampling s a ion 04. This inpu is again p obably ela ed o he ope a ion o he e ilize complex. In he case o Th, concen a ions a leas one o de o magni ude highe TABLE 3 Concen a ions o U and Th in Wa e Samples (pgl-‘) Collec ed Du ing Low Wa e , and Ac i i y Ra ios Sample [VI [Th/ 234 38 u 230 Th/232 Th Thl U 01 7.5 0.3 1.89 0.03 02 2.85 0.16 0.102 0.018 1.09 & 0.05 7.9 1.4 0.014 0.003 03 3.09 0.18 0.147 0.020 1.02 0.04 7.5 1 .o 0.048 & 0.007 04 6.9 & 0.4 8.4 . 1.0 1 .oo 0.05 5.4 * 0.02 1.22 0.16 05 5.3 0.3 0.58 0.19 1.06 0.09 11 z 4 0.11 0.04 06 4.5 0.3 0.29 0.05 1.09 &O.ll 5.8 1.1 0.064 0.012 07 4.98 z 0.24 0.14 0.02 1.08 z 0.04 7.4 1.2 0.028 0.004 E o s a e la. U anium and ho ium in an es ua y 287 han in o he non-pe u bed wo ld i e s (Moo e, 1967; Miyake e al., 1973) ha e been de ec ed. A high concen a ion peak (8.4pgl-‘) has been ound in sample 04, p obably ela ed o he ope a ion o he complex. The 234U/238U ac i i y a ios a e, in gene al, compa ible wi h he exis- ence o secula equilib ium. This is no he ypical disequilib ium obse ed in i e wa e s (Sco , 1982) bu is ypical o he mine als used o e ilize p oduc ion. The high a io obse ed in sample 01 mus be due o he highe end o 234U o be dissol ed. The 230Th/232Th ac i i y a io is abo e uni y all along he i e , indica ing g ea e con amina ion by adionuclides o he 238U adioac i e chain. Finally, he ThjU mass a io is, wi h he excep ion o sample 04, below uni y. This is consis en wi h he end o Th being associa ed wi h he solid phases in i e s. The excep ion mus be, as in he case o suspended ma e , ela ed o he con aminan s. This will be discussed la e , wi h he help o modelling. kd dis ibu ion coe icien s be ween suspended ma e and wa e o 238~ 232Th and 230Th a e p esen ed in Table 4. In he case o 238U, ou esul s a e in ag eemen wi h he alues ound in li e a u e. Indeed, kd o U in coas al wa e can ange om 0.2 o 5 lg-‘, he mean alue being 1 lg-’ (IAEA, 1985). The kds a e e y simila o bo h Th-iso opes, indi- ca ing ha hey a e dis ibu ed be ween wa e and suspended ma e in he same way. Howe e , alues below he ange o a ia ion which can be ound in he li e a u e (IAEA, 1985) ha e been ob ained. Ne e heless, a clea conclusion o hese esul s is he la ge kd a ia ion be ween di e en sampling poin s (up o wo o de s o magni ude). This a ia ion comes om he kd de ini ion i sel : i assumes an equilib ium si ua ion o he exchanges be ween he solid and liquid phases. This si ua ion is no always achie ed when an in-si u measu emen o kd is pe o med, especially in si es whe e he inpu in o he sys em is changing wi h ime (man-made pollu ion). Thus, when a kd measu emen is ca ied ou , an ex ensi e TABLE 4 Dis ibu ion Coe icien s (1 g-‘) o he Low-wa e Samples Sample 238 I/ 232Th 230Th 01 0.15 z 0.3 02 0.38 z 0.05 0.7 I 0.4 0.59 IO.17 03 0.91 * 0.12 0.7 4 0.3 0.91 0.17 04 12.5 z 1.6 13.8 1.8 13.3 S 1.6 0.5 4.8 IIZ 0.4 531 18 30 4 06 3.0 0.4 0.2 * 0.1 0.07 x 0.02 07 3.8 z 0.4 E o s a e lo 288 R. Pe i i iez, A. Ma inez-Agui e desc ip ion o he sampling condi ions (pH, empe a u e and salini y) should be made in o de o in e p e he esul . In open dynamic sys ems, such as in an es ua y, equilib ium condi ions will p obably ne e be eached. Thus, ma hema ical models designed o non-equlib ium condi- ions a e impo an ools o s udy he dispe sion o adionuclides in dynamic aqua ic sys ems. 4 THE MODELLING STUDY 4.1 Model desc ip ion The i s models which we e de eloped o s udy he dispe sion o non- conse a i e adionuclides in aqua ic sys ems we e a e aged box models in which he exchanges o adionuclides be ween he liquid and solid phases we e desc ibed in e ms o kd, assuming comple e equilib ium in he sys em (Howo h and Eggle on, 1988; Ab il & Ga cia-Leon, 1993). Howe e , in open sys ems whe e he inpu is changing wi h ime (as in he case o man-made pollu ion) and when s udying he dispe sion o adio- nuclides in small coas al egions (such as es ua ies), he equilib ium app oach will no hold. This is due o he ac ha , because o he high spa ial and empo al esolu ions ha a e imposed by he nume ical scheme, he equilib ium will no be eached in each ime s ep (Pe ia iez e al., 19966). In hese cases, a kine ic app oach is mo e app op ia e. Thus, he equilib ium will be he dynamic balance be ween wo opposi e chemi- cal eac ions (Ny ele e al., 1984). The model de eloped o s udy he dspe sion o adionuclides in he Odiel i e es ua y (which, o cou se, could be applied o any o he si e) makes use o his kine ic app oach. The model is p esen ed in de ail in Pe iaiiez e al. (1996b); hus, only a b ie desc ip ion o he p ocesses ha a e included will be gi en he e. The sys em unde s udy is di ided in o a numbe o g id cells o ‘compa men s’. Fou phases o subcompa men s a e p esen in each g id cell, which a e wa e , suspended ma e and wo sedimen g ain size ac ions. In Fig. 2, a g id cell is shown. Radionuclides can be dissol ed o associa ed wi h suspended ma e . As ides p oduce a con inuous mo emen o wa e , adionuclides in bo h phases will be anspo ed om one g id cell o ano he by ad ec i e and di usi e p ocesses. Only pa icles wi h a diame e 4 < 62.5 pm a e conside ed o be p esen in he wa e column as suspended ma e (Gu bu e al., 1987): la ge pa icles will apidly sink o he bo om. In sedimen s, we will conside wo g ain size ac ions: pa icles wi h diame e 4 < 62.5 ,um (small g ain size ac ion) and pa icles wi h 4 > 62.5 pm U anium and ho ium in an es ua y 289 ad ec ion and di usion 0 0 Fig. 2. G id .# ce lame ac ions cell in which he adionuclide ans e p ocesses be ween he ou phases a e ep esen ed. (la ge g ain size ac ion). Only he small g ain size ac ion can be esuspended in he wa e column and inco po a ed in o suspended ma e . On he o he hand, when suspended ma e is desposi ed on he es ua y bed, i will be inco po a ed in o he small g ain size ac ion o he sedimen s. Thus, he deposi ion and esuspension p ocesses p oduce an exchange o adionuclides be ween he suspended ma e and he small g ain size ac ion o he sedimen . The wa e is in con ac wi h he o he h ee phases; hus, adso p ion and deso p ion eac ions ake place. These eac ions a e desc ibed in e ms o kine ic ans e coe i- cien s. Finally, ex e nal sou ces o adionuclides (in dissol ed and suspended phases) may exis in each g id cell. We will conside ha he adso p ion p ocess ( ans e om wa e o he solid phases) is go e ned by a coe icien kl and he in e se p ocess (deso p ion owa ds he liquid phase) by a coe icien k2. The adso p ion p ocess is a su ace phenomenon and will depend on he su ace o pa icles pe wa e olume uni in o he g id cell. This quan i y will be deno ed he exchange su ace. I we now conside only suspended ma e as he solid phase (neglec ing sedimen s), we ha e: kl = xl &> (1) 296 R. Pe ihiez, A. Ma inez-Agui e 12 - ,' 1 : : I' 10 - ,' : ,jl : 8 2 ,' 8- s /' ,' ,/ 6- / ,/:: : IL 4- '! I' I ,I : ,' ' ,' '-_ 2- --.__.________,,.---_ ,I' L_ ,' NC __________________- m 0 I 1 I I I I I 0 0 5 10 15 20 25 30 35 40 Fig. 5, Compu ed (line) and measu ed (poin s) dis ibu ion coe kien (I g-‘) o U du ing low wa e . gene al beha iou o he Th/U mass a ios is well ep oduced by he model in all cases. I was men ioned in Sec ion 3 ha he U excess wi h espec o Th in suspended ma e indica es he exis ence o an ex e nal sou ce o U con amina ed pa icles o he i e . The e was, howe e , an E , I I I I 1 1 I 1.4 - exp. 8"s. - - A model susp. ---- model disc -- 1.2 - ,I' l- , ,' : /' : : . ' 0.8 - I' : I : : : : 0.6 - : (1 : : I' 0.4 - : '._ I' : __--__________ 1' 0.2 - ' ' ' L__/ __.-. I I I 0 5 IO 15 20 25 30 35 40 Fig. 6. Model esul s o Th dispe sion. (A) Wa e and suspended ma e du ing high wa e . (B) Suspended ma e du ing low wa e . (C) Wa e du ing low wa e . Concen a- ions a e gi en in pg 1-l and pg g-’ o wa e and suspended ma e samples, espec i ely. U anium and ho ium in an es ua y 297 F 140 1 I 1 I , I b =P. w B model ---- 120 - 100 I : - I : / / : 80 - : ) : : : , /j ,' : 60 - ,' ,' ,I' ,' 40 - ;p ,/' I 20 - ,' I' : ,' I' I ,/ : . . 0 5 10 15 20 25 30 35 40 I 9 c 8 exp. - model ---- 10 15 20 25 30 35 40 Fig. 6. Con inued. excep ion (samples SO4 and SO5 which we e he mos con amina ed). Indeed, mo e Th han U is discha ged in o he i e , in bo h dissol ed and suspended o ms. F om he second inpu a es ( he i s a e no indica i e because hey a e used jus o c ea e he backg ound), i can be shown ha , in solu ion, ThjU = 2.4, and in suspended ma e , Th/U = 1.5. Thus, mo e Th han U is discha ged and, as a consequence, he e is an excess o Th in wa e and suspended ma e nea he sou ce. Howe e , he e is an 298 R. Pe ibiez, A. Ma inez-Agui e 100 80 20 1 I I I I I I exp. - model ..~_ ,,-- >’ I ‘. ,/- Y_ I’ -._ _______.-._____-I --._________.----.-_ ok ” I I I I I I IA & 1 0 5 10 15 20 25 30 35 40 Fig. 7. Compu ed (line) and measu ed (poin s) dis ibu ion coe icien (1 g-‘) o Th du ing low wa e . excess o W in he es o he i e in bo h liquid and suspended phases. I seems clea ha he dissol ed Th ha is eleased o he i e is quickly ixed o solid pa icles, and hese pa icles ( oge he wi h he pa icles ha a e eleased om he sou ce and a e ich in Th) a e deposi ed on he i e 0.25 0.2 3 E 0.15 0.1 5.000000e-02 0 I - _‘.. .__________-.. ,,. ,--’ Y ,’ ,,’ ,,-- ‘ _‘ I’ -*_- ._,_‘- $I ,I’ 1, , , , ‘, : I’ i : .-. ,’ ----.__________--- ** i i ( , 0 5 10 15 20 25 30 35 40 Fig. 8. Compu ed (lines) and measu ed (poin s) ThjU mass a ios o suspended ma e samples du ing high wa e (A), wa e samples du ing low wa e (B), and suspended ma e samples du ing low wa e (C). U anium and ho ium in an es ua y 299 1.4 I I ! exP. 1-41 model ---- l.2- 0 0.6 - I' ,,' /' I' 0.4 - I' I' /' I ,' 0.2 - I' ,' : : ,,= ,' I : * /__-' .I_ 0. ________- ____---- I I ---___ _-----__-- _io___ 0 5 10 15 20 25 30 35 40 1.4- c ,’ __-- 4 cup. w model ---- ____-- , ,/-- 1.2 - ,' I ' ,' ' l- ,' I I' 0.6 - : 0.6 - ,' , I ‘ ' I' : ), : >/ 0.4 - : : : II #' : 0.2 - : j _____----..___I '. '.. o- e 1 I I I I ---___________T---g I I 0 5 10 15 20 25 30 35 40 Fig. 8. Con inued. bed nea he sou ce. In his way, a U excess would exis in he es o he i e , as con i med by he expe imen al and he model esul s. This hypo hesis is also suppo ed by he ac ha an excess o Th has been measu ed in sedimen s collec ed close o he e ilize complex (Ma inez- Agui e e al., 19946). The sensi i i y o he model o he di e en pa ame e s, he way o c ea ing he backg ound and he magni ude o he sou ce e m ha e al eady been s udied (Pe ia iez e al., 19943, 1996a,c). 300 R. Pe icinez, A. Ma inez-Agui e 5 CONCLUSIONS U anium and Th concen a ions ha e been measu ed in wa e and suspended ma e samples in an es ua ine sys em a ec ed by was e dispo- sal om a e ilize p ocessing complex. Dis ibu ion coe icien s ha e also been calcula ed. The esul s ha e shown a adioac i e impac and a signi ican kd a iabili y. In o de o pe o m a quan i a i e s udy on he dis ibu ion o U and Th, as well as on he kd a iabili y, a modelling s udy has been ca ied ou . The model includes he pa i ion o adio ace s be ween ou phases, and his pa i ion is based on a kine ic app oach. The model sol es he hyd odynamic equa ions, he suspended ma e equa ions and he ou equa ions ha go e n he ime e olu ion o he adio ace concen a ions in each one o he ou phases. The model esul s a e in good ag eemen wi h he expe imen al da a o bo h U and Th, and o bo h wa e and suspended ma e samples. The kd a iabili y is ep oduced by he model, as well as he ThjU mass a ios. This shows he goodness o he desc ip ion o he ans e p ocesses, since good esul s a e ob ained o elemen s wi h a e y di e en chemical beha iou (Ra, U, Th) by simply changing he alue o a pa ame e : he exchange eloci y. ACKNOWLEDGEMENTS This wo k was pa ially suppo ed by ENRESA. The au ho is indeb ed o J. M. Ab il o help in he modelling wo k. REFERENCES Ab il, J. M. & Ga cia-Leon, M. (1993). A 2D-4 phases ma ine dispe sion model o adionuclides. Pa 1: concep ual and compu a ional model. J. En i on. Radioac ., 20, 71-88. Be ine, K. K., Chan, L. H. & Tu ekian, K. K. (1970). U anium de e mina ions in deep-sea sedimen s and na u al wa e s using ission acks. Geochim. Cosmochim. Ac a, 34, 641-8. Bha , S. G. & K ishnaswamy, S. (1969). Iso opes o u anium and adium in Indian i e s. P oc. Indian Acad. Sci., 70, 1-17. Fla he , R. A. (1994). A s o m su ge p edic ion model o he no he n bay o Bengal wi h applica ion o he cyclone disas e in Ap il 1991. J. Phys. Oceanog ., 24, 172-90. Fla he , R. 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Pugh, D. T. (1987). Tides, Su ges and Mean Sea Le el. John Wiley, Chiches e . Sco , M. R. (1982). The chemis y o U- and Th-se ies nuclides in i e s. In U anium Se ies Disequilib ium: Applica ions o En i onmen al P oblems, eds M. I ano ich & R. S. Ha mon. Cla endon P ess, Ox o d, pp. 181-201. Van de Heijde, H. B., Klijn, P. J. & Passchie , W. F. (1988). Radiological impac s o he disposal o phosphogypsum. Radia . P o . Dosim., 24, 419- 23. APPENDIX Dissol ed phase acL4 ---Z a -ki Cd j!$ + k2 C,m g + k2 (sed, + sedi) + (ad + di ), (Al) whe e Cd and C, a e he adionuclide concen a ions in wa e (mgmh3) and suspended ma e (mgg-‘), espec i ely, m is he suspended ma e concen a ion (mgl-‘) and H is he wa e column heigh . The ime de i- a i e mus be in e p e ed as in a o wa d ini e di e ences scheme. The * means ha he co esponding quan i y mus be e alua ed in he new ime s ep. The i s e m ep esen s he ans e o adionuclides om wa e o he h ee solid phases. Thus, kl is gi en by eqn (3). ad + di ep esen s ad ec i e plus di usi e anspo o dissol ed adionuclides om one g id cell o ano he . The hi d e m is he ans e o adionuclides om he wo ac ions o sedimen s o wa e : sed s H* sed I (A21 (A3) whe e a, and aI a e he adionuclide concen a ions in he small and he la ge g ain size ac ion o he sedimen s, espec i ely (mgg-*). The bulk densi y o he sedimen , pm, is gi en in kgme3. U anium and ho ium in an es ua y Suspended ma e 303 acs a = m*H* kl x - k2Cs s + ( es - dep) + (ad + di ). (-44) As he i s e m is he ans e o adionuclides om wa e o jus suspended ma e , kl is gi en by he i s e m o eqn (3). ad + di is he ad ec i e plus di usi e anspo o adionuclides in suspended ma e . The second e m is he ans e o adionuclides om suspended ma e o wa e , and es and dep ep esen he esuspension and deposi ion p oces- ses: d C,m dep = - m*H* iws 9 es = ___ m*H’ ( > -- I 103, VC, (A% whe e d and , a e he mean deposi ion and esuspension eloci ies, Cd and ,, a e he c i ical deposi ion and esuspension eloci ies and q is he wa e lux eloci y. Bo h in he dissol ed phase and in he suspended ma e equa ions, he ex e nal sou ces o adionuclides mus be included in he g id cells in which hey exis . Sedimen s The equa ion o he small g ain size ac ion is: &I, CdH a = kl - P& lo3 - kza, ,b + (dep - es). (A7) The i s e m is he ans e om wa e o he small ac ion o he sedi- men . Thus, kl is gi en by he second e m o eqn (3). The second e m is he ans e o adionuclides om he sedimen o wa e and dep - es ep esen s he ans e s be ween he sedimen and suspended ma e ( h ough deposi ion and esuspension): dep = (A@ a, ( > z-1 es = 7 ,, . (A9) 304 R. Pe ici ?ez, A. Ma inez-Agui e The equa ion o he la ge g ain size ac ion o he sedimen is: 8 al a = (AlO) whe e he i s e m is he ans e o adionuclides om wa e o he sedimen [kl is gi en by he hi d e m o eqn (3)], and he second e m ep esen s he in e se p ocess.