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Experimental and modelling study of artificial radionuclides (239Pu, 241Am and 99Tc) uptake by suspended matter in environmental waters located in the south of Spain

Abstract

The interest on transfer coefficients studies have increased recently, since they are important parameters required understanding and reliably modelling the dispersion of conservative and non-conservative radionuclides in aquatic environments. The approaches, based in the implementation of the uptake kinetics of dissolved radionuclides by solid particles, are more appropriate than those based in the use of the distribution coefficients, k^. In this work, we present a series of tracing experiments to study the uptake of Pu, Am and Tc in natural aqueous suspensions from three aquatic systems (Gergal reservoir, Guadalquivir river, and the estuary of Tinto river) located in the South of Spain. The kinetic transfer coefficient for direct sorption depends on the total available surface of particles and on the concentration of active sites in the surface layer (what depends on the mineral composition, free edges, pores, coatings, etc.). In order to compare results from different environments and to fix the conditions of applicability of the derived coefficients, it is necessary to handle the particle size spectra and the mineral composition of natural occurring suspended loads. The time dependent uptake curves, covering up to a large period, are fitted to the numerical solutions calculated with different models of the uptake kinetics.

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Experimental and modelling study of artificial radionuclides (239Pu, 241Am and 99Tc) uptake by suspended matter in environmental waters located in the south of Spain

Author: El Mrabet, Rachid; Abril Hernández, José María; Manjón Collado, Guillermo
Publisher: E. D. P. Sciences
Year: 2002
DOI: 10.1051/radiopro/2002112
Source: https://idus.us.es/bitstreams/63d0a758-47f8-4576-81c0-b453d64a33d2/download
Radiop o ec ion - Colloques, olume 37, Cl (2002) Cl-81
Expe imen al and modelling s udy o a i icial adionuclides
(239Pu,241 Am and 99Tc) up ake by suspended ma e in en i onmen al wa e s
loca ed in he sou h o Spain
R. El-M abe , J.M. Ab il1 and G. Manjon2
Depa amen o de Física A ómica, Molecula y
Nuclea ,
Facul ad de Física,
Uni e si y o Se ille, Apdo., 41060 Se illa, Spain
1 Depa amen o de Física Aplicada 1, Uni e si y o Se ille, EUITA,
Ca e e a de U e a km 1, 41013 Se illa, Spain
2 Depa amen o de Física Aplicada 2, Uni e si y o Se ille, ETSA,
A da. Reina Me cedes s/n, 41012 Se illa, Spain
Abs ac . The in e es on ans e coe icien s s udies ha e inc eased ecen ly, since hey a e impo an pa ame e s
equi ed unde s anding and eliably modelling he dispe sion o conse a i e and non-conse a i e adionuclides in
aqua ic en i onmen s. The app oaches, based in he implemen a ion o he up ake kine ics o dissol ed
adionuclides by solid pa icles, a e mo e app op ia e han hose based in he use o he dis ibu ion coe icien s, k^.
In his wo k, we p esen a se ies o acing expe imen s o s udy he up ake o Pu, Am and Tc in na u al aqueous
suspensions om h ee aqua ic sys ems (Ge gal ese oi , Guadalqui i i e , and he es ua y o Tin o i e ) loca ed
in he Sou h o Spain. The kine ic ans e coe icien o di ec so p ion depends on he o al a ailable su ace o
pa icles and on he concen a ion o ac i e si es in he su ace laye (wha depends on he mine al composi ion, ee
edges,
po es, coa ings, e c.). In o de o compa e esul s om di e en en i onmen s and o ix he condi ions o
applicabili y o he de i ed coe icien s, i is necessa y o handle he pa icle size spec a and he mine al
composi ion o na u al occu ing suspended loads. The ime dependen up ake cu es, co e ing up o a la ge pe iod,
a e i ed o he nume ical solu ions calcula ed wi h di e en models o he up ake kine ics.
1.
INTRODUCTION
In e es in Pu, Am and Tc up ake kine ics in na u al aqueous suspensions has ecen ly inc eased in
o de o unde s and and eliably model he dispe sion o adioac i e was es in aqua ic en i onmen s,
especially when kine ic eac i e anspo models o idal wa e s a e used [1]. The app oaches based on
he implemen a ion o he up ake kine ics a e mo e app op ia e han hose based on he use o dis ibu ion
coe icien s, kd. Mo eo e , [2] ha e discussed he cons ain s o he applicabili y o "in-si u dis ibu ion
coe icien " alues in he quan i ica ion o solu e anspo in na u al wa e s.
In he scien i ic li e a u e we can ind many examples o expe imen al s udies on he up ake kine ics
o dissol ed adionuclides by suspended loads. Thus, [3] ob ained kine ic ans e coe icien s o se e al
elemen s om seawa e on o pa icula e ma e and su ace sedimen s by using a model o wo
consecu i e and e e sible eac ions and con ac imes o se e al weeks. [4] s udied he e ec s o changes
in suspended ma e concen a ions and empe a u e on he kine ic ans e coe icien s o Co and S and
discussed he use o models o wo pa allel and wo consecu i e eac ions. [5] published he expe imen al
de e mina ion o kine ic ans e coe icien s o 133-Ba in es ua ine wa e s and s udied he e ec s o
salini y and suspended load concen a ions. Al hough o he au ho s ha e no ob ained ans e
coe icien s, hei s udies ha e included he e ec o sedimen ype, empe a u e, colloids, pa icle size
and pa icle concen a ion on he up ake o adionuclides by sedimen s.
The p esen s udy epo s he esul s o ace expe imen s wi h 2WPu, 241 Am and MTc in un il e ed
wa e s om h ee aqua ic sys ems in sou he n Spain. The expe imen al p ocedu e e ains he na u al
condi ions, and Pu ac i i y is measu ed by liquid scin illa ion.
2.
MATERIAL AND METHODS
De ails conce ning he sampling, he physic-chemical cha ac e isa ion o samples and he
expe imen al and analy ical p ocedu es we e p esen ed in a p e ious wo k [6], Consequen ly, we will
b ie ly desc ibe he e only he mos ele an aspec s.
Wa e samples we e collec ed om h ee di e en aqua ic scena ios om he Sou h o Spain. The
i s s a ion was loca ed he Ge gal ese oi (NW om Se ille). The second sample was collec ed in he
Guadalqui i i e , nea he own o Se ille. Finally a hi d sample was collec ed in he Tin o es ua y,
close o he A lan ic Ocean, du ing he low ide.
A each sample si e, we illed ou 25
1
plas ic bo les. Tempe a u e, pH and elec ical conduc i i y we e
measu ed jus a e collec ion. Samples we e hen ca ied o ou labo a o y and s o ed in da k du ing ew
hou s.
The acing expe imen s gene ally begun a he ollowing mo ning. We used a nephelome e o
measu e he suspended ma e con en .
Cl-82 RADIOPROTECTION - COLLOQUES
In each expe ience, a ypical olume o 1.0
1
o wa e was ans e ed in o a glass beake . The e, he
sample was spiked wi h 239Pu, 241Am o "Tc and con inuously s i ed in o a oid any décan a ion o he
suspended ma e . We ollowed he ime e olu ion o he ac i i y concen a ion in he dissol ed phase by
aking aliquo s a di e en imes a e spiking. A ypical olume o 45 ml was selec ed o e e y aliquo .
Suspended ma e was emo ed by cen i uga ion (20 minu es a 4000 pm). Then, 35 ml o supe na an
we e ans e ed in o a plas ic con aine and acidula ed wi h 1ml o HN03 o a oid loses o plu onium by
adso p ion on o he con aine walls. Finally, 5 ml o acidula ed sample was ans e ed in o a plas ic ial
and mixed wi h 15 ml o liquid scin illa ion cock ail Pha macia Op iphase 3.
A g anulome ic analysis o all he samples was ca ied ou by using a Mas e Size ins umen wi h
100 size bands, om 0.01 o 1000 um. A Scanning elec on mic oscope (SEM) wa^^se^ o s udy he
mo phology o na u al pa icles om all he samples.
Resul s om expe imen s wi h 239Pu a e depic ed in Fig. 1, which shows he ime cou se o he o al
239Pu ac i i y (gi en in cpm) in 5 ml in he supe na an wa e s.
•5
Ri e (1) ~—i
><—
Ge gal (1)
Es ua y <
Ge gal (2)
Ri e (2)
M»-.
h }
(d) *}
1
0.01 0.1 1 10 100
Time (hou s)
Fig. 1: Time e olu ion o I59Pu ac i i ies (in cpm) in he dissol ed phase co esponding o he i e expe imen s (poin s wi h
e o
ba s).
Con inuous lines indica e he di e en sequences o (he up ake kine ics.
3.
MODELLING APPROACHES
In wha ollows we will apply o ou da a a model o wo pa allel, e e sible and concen a ion-
independen eac ions ollowed by a consecu i e, non- e e sible and concen a ion-independen eac ion
o de i e he co esponding alues o he kine ic coe icien s (see discussion in sec ion 4). The equa ions
o he sys em a e:
=
-(*!.!
+ *1J K + *2ja
T.l + K2.2 "V,2
a
da ,
i
ia
= *l.l l. -*!.ia,,.l -*!.ia„,l
= *l,l°» -*2jO».2_*3.2a».2
(1.1)
(1.2)
(1.3)
da sp j
d = k,
,a,„,
+ k* ,am < 4
whe e aw [Bq/1] is he ace concen a ion in he dissol ed phase;
aspj
and
aSpj
[Bq/1] a e he
concen a ions ela ed o si es in solids pa icipa ing in i s and in second pa allel and e e sible
ECORAD 2001 Cl-83
eac ions, espec i ely. Simila ly,
aS >
3 [Bq/1] is he concen a ion in solids ela ed o he non- e e sible
unions. The six kine ics ans e coe icien s ha e uni s in e sely p opo ional o ime (s' o h"1). In he
i s ins ance we assumed a simila alue o £37 and ¿32 coe icien s. The concen a ions in solids a e
ela ed o he co esponding speci ic ac i i ies ( in Bq/kg and deno ed wi h *) by means o suspended load
concen a ion, ms, in uni s o
kg/1:
asp,l = a sp.l ms-> asp,2 = a sp,2 ms, and
asp,3=a*sp,3nis ' ,
We s a ed some ini ial alues o kine ic coe icien s in a compu e code ha nume ically sol es
equa ions 1.1 o 1.4. The pa ame e alues a e hen a ied o ge he bes i (i.e., minimises he
summa ion o he weigh ed squa ed di e ences be ween nume ical solu ion and obse a ional da a
poin s). As each pa hway is dominan o e a egion (o in e al) in he up ake cu e, an o e all pa ame e
i ing is no ad isable. Thus, he i is sequenced egion by egion and hen e ined o e all. The
g aphical ep esen a ion ensu es he quali y o he solu ion. The so de i ed pa ame e alues a e
summa ised in Table 1.
Table
1.- Pa ame e alues a e i ing expe imen al da a ( o case o 239-Pu) o a model o wo pa allel plus a consecu i e
and
non- e e sible
eac ion.
The esul o
he
x- es
o he i ing is shown in he las
column.
Expe imen k„(h-') Kii(h ) ku(h-')
Es ua y, 2 days, /.62 ppm 1.9 8.2 o.iy 0.28 0.0005 1.03
(ie gal, 2 days, 1.5
1
ppm 1.1 2.6 0.05 0.25 0.009 0.95
Ki e , 2 days, 12.6 ppm 12.3
17
o.oy 0.20 0.055 1.55
In Figs. 2 o 6 we show he nume ical solu ion o expe imen s wi h Pu, Am and Tc.
4.
DISCUSSION
F om Fig. 1 (in case o Pu), in loga i hmic scale, h ee di e en egions cha ac e ised by di e en slopes
can be dis inguished: egion (a) co esponds o a as eac ion, las ing o ew minu es, du ing which ime
up o 30% o dissol ed Pu is ans e ed on o suspended solids. This co esponds o a as physical-
adso p ion eac ion (Pu is ixed by coulombian o ces on o he ex e nal ee su ace o pa icles); in
egion (b), a second eac ion go e ns he Pu up ake du ing 10-20 hou s ime, ans e ing up o 30% o
emaining Pu in dissol ed o m. This eac ion co esponds o physical adso p ion on o he inne su ace
o po es and ee-edges, and o he o ma ion o e e sible unions o a di e en na u e and/o s eng h. In
egion (c), he up ake (up o 50% o he emaining Pu in solu ion) con inues du ing se e al days ( he
du a ion o he expe imen s was oo sho o allow a conclusion conce ning he inal cou se o he
eac ion). This eac ion may co espond o a slowe p ocess in which p e iously adso bed Pu is
ans e ed in o he inne ma ix o he pa icles o o ms o he non- e e sible unions. Region (d)
co esponds o a as e up ake o Pu om he dissol ed phase. I is obse ed only in he i s expe imen
wi h i e wa e s and may be ela ed o loccula ion e ec s.
We obse e he same si ua ion in case
o 241
Am. "Tc is conside ed as conse a i e adionuclide and
he beha iou is di e en han o he Pu o Am.
In all cases (Pu and Am), he i s pa allel eac ion is he as e . I ans e s an impo an ac ion o
he dissol ed adio ace o he pa icula e phase, kjj is he a e o adso p ion, and depends on he o al
a ailable su ace o pa icles pe uni olume o solu ion (which in u n go e ns he numbe o physical
collisions and hus, kjj should be p opo ional o mSi i he es o physical-chemical p ope ies we e
p ese ed), and on hé concen a ion o ac i e a eas (which go e ns he p obabili y o eac ion). The
physical meaning o kjj and ¿2,2 's na ° a p obabili y o deso p ion, which implies he up u e o
physical-chemical unions in si es associa ed wi h he wo pa allel eac ions. F om ou in e p e a ion, kj 2
does no depend di ec ly on he o al ee su ace o pa icles, bu also on he exis ence and geome y o
po es and ee edges and he accessibili y o he eac ion si es. The hi d eac ion is go e ning he long-
e m beha iou o he pa i ion coe icien , k^. E ec i ely, he ans e o adionuclides o he inne ac i e
a eas ees he si es hey occupied in he su ace laye o pa icles. This enhances he up ake o
adionuclides by he pa icula e ma e .
Cl-84 RADIOPROTECTION - COLLOQUES
.a
Fig.2:
Time e olu ion
o
Pu
ac i i ies
(in
cpm)
in he
dissol ed phase co esponding
o he
sé ie
o
expe imen
o
he case
o
he Ge gal ese oi . Measu ed alues appea s wi h e o
ba s,
while con inuous line co esponds o he bes i o
he
model.
20
30
Time (hou s)
Fig.3:
As in
Figu e
2 bu o
he case
o
he
Guadalqui i i e
3
0
10
F g.4:
As in
Figu e
2
bu
o
he case o he Tin o es ua y
ECORAD 2001
CI-85
20
25 30
40
45 50
FigS:
As in
Figu e
2 bu
wi h 141
Am, o
he case
o
he
Guadl^u'wi n e
16l
. , , . . . , 1
0
5 10 15 20 25 30 35 40
Time (hou s)
Fig.6:
As in
Figu e
2 bu
wi h
**Tc,
o he
case
o
he
Guadalqui i i e
5.
CONCLUSIONS
L- In his wo k we applied a use ul expe imen al p ocedu e o s udy he up ake o Pu, Am and Tc by
na u al aqueous suspensions, based on he use o liquid scin illa ion echnique.
2.-
By using a model o a single and e ec i e oxida ion s a e, wi h wo pa allel e e sible and
concen a ion-independen eac ions, ollowed by a consecu i e non- e e sible eac ion, we ob ained
a easonable unde s anding o he up ake cu es.
3.-
We ha e p o ided a se o kine ic pa ame e s use ul o desc ibe he mos ele an aspec s o he
elec oly ic eac ions o "9Pu,241 Am and "Tc in he aqua ic en i onmen s s udied unde en i onmen al
condi ions p e ailing du ing he sampling.
4.-
The expe imen al esul s show ha each pa hway o eac ion is go e ning he up ake a di e en
s ages, and some possible in e e ing and/o modi ying ac o s a e iden i ied (s o age, loccula ion,
compe i i e ions). This p o ides a good basis o imp o e he expe imen al se up o p oduce mo e
accu a e alues o kine ic pa ame e s

Cl-86 RADIOPROTECTION - COLLOQUES
Acknowledgemen s
This wo k has been pa ially suppo ed by I+D con ac wi h ENRESA, Spain.
Re e ences
1.
Pe iá iez R. Jou nal o Ma ine Sys ems 22 (1999)
37-51.
2.
Mckinkley I.G. and Alexande W.R. Jou nal o En i onmen al Radioac i iy 15 (1992) 19-34.
3.
Ny ele U.P, Yuan-Hui Li and San shi P.H. Geochim. Cosmochim. Ac a 48 (1984) 1513-1522.
4.
Benes P., Cemik M. and Lam Ramos P. Jou nal o Radioanaly ical and Nuclea Chemes y. 159(2)
(1992) 201-218.
5.
Laissaoui A., Ab il J.M., Pe iáñez R., Ga cía León M., Ga cía Mon ano E. Jou nal o Radioanaly ical
and Nuclea Chemes y. 237 (1-2) (1998)
55-61.
6. R. El M abe , J.M Ab il, G. Manjón and R. Ga cía Teno io. Wa e Resea ch (2001) (accep ed o
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