scieee Science in your language
[en] (orig)

The distribution of U, Th and 226Ra derived from the phosphate fertilizer industries on an estuarine system in Southwest Spain

Abstract

This paper reports an extensive study of the presence of natural radioactivity around a phosphate fertilizer factory complex situated in an estuarine area of southwest Spain. The study has concluded that the wastes from such industries are the cause of the enhancement of natural radioactivity in the immediate environment. Thus, significantly high levels of U- and Th-isotopes and 226Ra are detected in water and sediment samples collected in this area. These conclusions based on the enhanced isotopic concentrations are further supported by the measured different from any observed elsehwere in undisturbed estuaries. These isotope activity ratios appear to be very sensitive indicators of waste disposal practices in such environments.

Read accessible full text

The distribution of U, Th and 226Ra derived from the phosphate fertilizer industries on an estuarine system in Southwest Spain

Author: Martínez Aguirre, Aránzazu; García León, Manuel; Ivanovich, M.
Publisher: Elsevier
Year: 1994
DOI: 10.1016/0265-931X(94)90020-5
Source: https://idus.us.es/bitstreams/483ebd81-853d-4a04-914b-02cfc7eeb235/download
The Dis ibu ion o U, Th and 226Ra De i ed om he
Phospha e Fe ilize Indus ies on an Es ua ine Sys em in
Sou hwes Spain
A. Ma ínez-Agui e, M. Ga cía-León
Facul ad de Física, Uni e sidad de Se illa, Apa ado 1065. 41080 Se illa, Spain
&
M. I ano ich
AEA En i onmen and Ene gy, Ha well Labo a o y, Oxon OXI 1 ORA. UK
ABSTRACT
This pape epo s an ex ensi e s udy o he p esence o na u al adioac i i y
a ound a phospha e e ilize ac o y complex sí ua ed in an es ua ine a ea
o sou hwes Spain. The s udy has concluded ha he was es om such indus ies a e
he cause o he enhancemen o na u al adioac i i y in he immedia e en i onmen .
Thus, signi ican ly high le els o U- and Th-iso opes and 226 Ra a e de ec ed in wa e
and sedimen samples collec ed in his a ea. These conclusions based on he enhanced
iso opic concen a ions a e u he suppo ed by he measu ed U, Th and Ra iso opic
ac i i y a ios being qui e di e en om any obse ed e sewhe e in undis u bed
es ua ies. These iso ope ac i i y a ios appea o be e y sensi i e indica o s o was e
disposal p ac ices in such en i onmen s.
INTRODUCTION
Recen ly, se e a! s udies ha e been ca ied ou in he icini y o phospha e
e ilize indus ies in a de o es ablish he signi icance o he adiological
impac o hei ope a ions on he en i onmen as well as on he human
popula ion (S ain, 1979; Van de Heidje e al., 1988; Kos e e al., 1991;
Ma ínez-Agui e & Ga cía-León, 1991a). While ypical ocks con ain on
a e age so ne 2·8 ppm o U (UNSCEAR, 1977), a phospha e ock can
con ain up o 50-300 ppm o U (Gascoyne, 1982). The Eu opean
Communi y impo s annually so ne 15-17 MT o phospha e ock
(Baes slé, 1991 ). The impo ed ma e ial is p ocessed in o di e en
p oduc s gene a ing was es such as phosphogypsum. Each yea 6-7 MT
o phosphogypsum is discha ged di ec ly in o he sea, and, in addi ion,
so ne 8-11 MT is deposi ed as so lid was es in piles (Baes slé, 1991 ). These
piles emain unp o ec ed om ainwa e , wind and o he elemen s, and
hus hey could be connec ed hyd aulically o su ace o g oundwa e s as a
po en ial sou ce o con amina ion.
The phosphogypsum is mainly composed o CaS04. This means ha i
also con ains U, Th and Ra in la ge quan i ies as a esul o co-p ecipi a ion
wi h Ca du ing he p ocess o e ilize p oduc ion. I is he e o e possible
ha na u al p ocesses could lead o he edis ibu ion o hese na u al
adionuclides in o he en i onmen su ounding he was e disposal si es.
S ain ( 1979) ound a signi ican inc ease o Ra ac i i ies in g ound
wa e s collec ed a ound a e ilize ac o y a No h Ca olina, USA. So ne
o he wo ke s (Van de Heidje e al., 1988; Kos e e al., 1991) ha e also
s udied he p esence o na u al adioac i i y, mainly 226Ra and 21 ºPo, in
Eu opean en i onmen s a ec ed by such indus ies. Also, Paul e al. (1980)
in es iga ed signi ican ly high 226Ra concen a ions in phosphogypsum a
Ke ala, India.
Recen ly, Ma ínez-Agui e and Ga cía-León (1991a) ound anoma
lously high U-iso ope ac i i ies in wa e and sedimen samples collec ed a
he Odie! and Tin o i e s in sou hwes Spain (Figs 1 and 2). Such
enhancemen s we e a ibu ed o an indus ial complex su ounded by
hese i e s in which wo phospha e e ilize ac o ies we e loca ed. One
ac o y p ocesses a ound 1-4 MT pe yea o phospha e ock om
Mo occo, while he o he uses a ound 0·2 MT o ock om Mo occo,
Senegal and Togo. Bo h ac o ies elease hei was es di ec ly o he Odie!
i e o a e s o ed in unco e ed piles ( he a ea ma ked wi h s a s in Fig. 2).
U sing he da a gi en by Guimond and Ha din (1989) o phospha e ock
om Mo occo, he i s ac o y alone may p oduce a ound 2-2 TBq o
226Ra, 2-3 TBq o 238U and 1 -4 TBq o 232Th each yea . Pa o his ac i i y
can ob iously be edis ibu ed o e he en i onmen ha su ounds he
indus ial complex.
This pape ep esen s a mo e comple e s udy o possible edis ibu ion o
he adioac i i y om he was es gene a ed by he abo e phospha e
e ilize ac o ies. To his pu pose iso opes o U and Th and 226Ra ha e
been ex ac ed and de e mined om di e en su ace wa e and sedimen
Medi e anean sea
Fig. l. Map o Spain showing he s udied a ea in he Andalousian egion.
collec ed du ing 1989. The adionuclide concen a ions in hese samples
and he co esponding ac i i y a ios, which e lec he daugh e s mobili y,
and p obably, also he o igin o he adionuclides, will be used o
in es iga e he dis ibu ion o adioac i i y o e his a ea o sou hwes e n
Spain.
SAMPLING AND EXPERIMENTAL METHODS
Samples o i e wa e and sedimen we e collec ed along he Odiel and
Tin o i e basins (Fig. 2) du ing July 1989. Su ace wa e samples o 7-1 O l
we e collec ed in plas ic bo les du ing low ide, and pH and empe a u e
(ºC) we e measu ed a he same ime. The suspended ma e was sepa a ed
as soon as possible using 0-45 µm po e size Nuclepo e il e s. I has been
p ese ed o u u e analysis, since i could p o ide in e es ing addi ional
in o ma ion. Then, he il a e was acidi ied o pH ""2 by concen a ed
HN03, o a oid he g ow h o mic oo ganisms and o minimize wa e /wall
in e ac ions. A he same ime, bo om sedimen s we e collec ed. Samples
o abou 1 kg we e collec ed and s o ed in plas ic bags. Then, in he
labo a o y, sub-samples we e d ied and powde ed be o e analysis.
The ex ac ion me hod used o U- and Th-iso ope sepa a e is gi en in
® Piles o phosphogypsum
O 3km
L____J__j
Fig. 2. Map o Odiel and Tin o i e s showing he sampling s a ions in 1989.
I ano ich and Mu ay (1992) and Ma ínez-Agui e (1991). Only a b ie
desc ip ion is gi en he e. A e homogeniza ion, a ew g ams o d y
sedimen , spiked wi h known quan i ies o 236U and 229Th s anda d
solu ions o chemical yield de e mina ions, a e diges ed wi h HN03, aqua
egia, HC104 and HF. The esidue le a e he abo e ea men is
dissol ed in 7M HN03. The U and Th a e co-p ecipi a ed wi h Fe3+ by
adding concen a ed ammonia o he solu ion. The U- and Th-iso opes a e
i s sepa a ed by using anion exchange esins (Dowex AG 1 X 8
hyd ochlo ic o m) condi ioned wi h 8M HCl. Then each ac ion is
u he pu i ied by he emo al o Fe whose p esence would a ec he .x
spec al esolu ion. Fo his las pu i ica ion s ep he esins in he
sepa a ion columns a e condi ioned wi h 7M HN03. These pu i ied
solu ions a e d ied and U and Th a e elec opla ed on o s ainless s eel
planche s using he p ocedu e o Lally and Eakins (1978). The ac i i ies a e
de e mined by a-spec ome y using su ace ba ie Si a-de ec o s.
In he case o wa e samples, so ne 7-101 o wa e a e spiked wi h 236U
and 229Th s anda d solu ions and hen boiled down o app oxima ely 11.
The U and Th con en is hen co-p ecipi a ed wi h Fe3
+ by he addi ion
o (NH)40H. The p ecipi a e, a e sepa a ion om supe na e by con i
uging, is dissol ed by 7M HN03. Finally, he same p ocedu e, desc ibed
abo e o diges ed solid samples, is ollowed.
Fo he 226Ra analysis in sedimen samples, he 222Rn emana ion me hod
was used. The samples a e i s diges ed wi h HN03, aqua egia, HC104
and HF and hen he esidue is dissol ed wi h 8M HCl and he olume made
up o 0-51. The solu ion is hen ans e ed in o a sealed glass bo le and he
o iginal c op o 222Rn expelled by bubbling ul apu e He gas h ough. A e
app oxima ely h ee weeks secula equilib ium be ween a new c op o
222Rn and 226 Ra in solu ion is eached. The 222Rn is again expelled and
collec ed in a ZnOz-lined qua z coun ing cell. The 222Rn ac i i y is
measu ed by a gas scin illa ion coun e and om i he 226Ra concen a ion
in he sample is de e mined (I ano ich & Mu ay, 1992).
RESULTS AND DISCUSSION
As al eady s a ed, he indus ial zone unde s udy is si ua ed on a ongue o
land su ounded by he i e s Odiel and Tin o, wi h hei con luence a i s
ip (Fig. 2). The wo i e s a e a ec ed di e en ly by he indus ial ac i i y.
Consequen ly, he p esen a ion and he discussion o he esul s will be
ca ied ou sepa a ely o each i e . In he ables and igu es he au ho s
ha e deno ed wi h 'O' and 'SO' he wa e and sedimen samples,
espec i ely, om he Odie! i e . Simila ly, o he Tin o i e samples,
p e ix le e 'T' and 'ST' ha e been used. P e ix le e s 'OT' and 'SOT'
co espond o samples de i ed om he con luence o he wo i e s which
o ms a common mou h o he A lan ic Ocean. The numbe s gi en o each
sample iden i y he sampling s a ion (Fig. 2).
In addi ion o he U and Th iso opic ac i i ies exp essed in mBq/1 ( o
wa e samples) o mBq/g ( o sedimen samples), U and Th mass
concen a ions a e also gi en in µg/1 o µg/g. The wo a e ela ed by he
ollowing con e sion o mulae:
[U] = 0-08 l lA23s
[Th] = 0-2436A232
(1)
(2)
whe e [U] and [Th] a e he mass concen a ions and A238 and A232 a e he
ac i i ies o 238U and 232Th, espec i ely.
Odiel i e
The sampling s a ions a e dis ibu ed along he lowe eaches o he i e
close o he indus ial zone a ea (Fig. 2). The excep ion is s a ion 1 which is
si ua ed a ups eam o his a ea close o he i e sou ce.
Wa e
The U- and Th-iso ope ac i i ies a e gi en in Table 1 oge he wi h pH
alues. I is appa en ha all adionuclides measu ed in he collec ed wa e

TABLE 1
U- and Th-Iso ope Ac i i ies (m/Bq/1) and pH o Wa e Samples Taken Along he Odiel Ri e
238Th
Sample pH 23su 234u 232Th 230Th
01
3-01 197·9 ± 6·8 316-3 ± 10-7 13-4 ± 0-6 49.7 ± 1-7 22-9 ± 0-9
02 7-40 34-2 ± 1-1 36-3±1-2 0-58 ± 0-30 7-02 ± 1-33 2-65 ± 0-78
03 7-20 33·0 ± 2-0 35-0 ± 2-1 1-81 ± 0-14 12-0 ± 0-5 NM
NM
04 7-12 54·1 ± 3.4 58-7 ± 3.7 2-21 ± 0-24 14-3 ± 0-7
05 7-08 52·7 ± 3-6 54.3 ± 3.7 2-51 ± 0-25 18-9±1-3 7-52 ± 1-20
8-83 ± 2-89
2-38±0-15
06 6-80 131-3±11-3 136-2± 11-7 4.73 ± 0-67 34-2 ± 3.3
07 6-96 35-8 ± 0-9 39-2 ± 0-9 1-83±0-12 11-2±0-4
NM, No measu ed.
sample ollow he same dis ibu ion pa e n along he i e wi h wo well
de ined peaks.
The iso opic da a ob ained o sample O 1 a e anomalous ela i e o he
es o he da a se . The e y low pH alue o 3, due o local geology
condi ions, accoun s o he obse ed enhanced concen a ion lis ed. The
head wa e s o i e Odiel a e chemically agg essi e, esul ing in e ec i e
leaching and ans e o U and Th om he solid o he aqueous phase o
he sys em. The Th iso opes, mainly insoluble in na u al wa e s, ha e
concen a ions a leas one o de o magni ude highe han in a e age
su ace wa e s (Ma ínez-Agui e & Ga cía-León, 1992; Osmond &
l ano ich, 1992), e lec ing he highe mobili y o Th a e y low pH alues.
Highe concen a ions o U- and Th-iso opes also pe sis downs eam
be ween sampling s a ions 04 and 06, wi h a clea peak o ac i i y a
sampling s a ion 06. A simila pa e n was obse ed o U-iso opes in
samples collec ed in 1988 (Ma ínez-Agui e & Ga cía-León, 1991a). The
obse ed pa e n is indica i e o he exis ence o a local sou ce be ween
s a ions 04 and 06. The ob ious candida e o his local sou ce o
adioac i i y has o be ela ed o he phospha e manu ac u ing complex
loca ed be ween s a ions 04 and 05. The obse ed shi in he loca ion o
he peak o ac i i y om s a ions 05 and 06 in he wo sampling campaigns
is a esul o a lowe idal inpu and a highe ac i i y inpu (highe was e
ou pu om he phospha e ac o ies) o he i e a he ime o sampling.
This si ua ion was encoun e ed du ing he 1988 sampling campaign when
he ac i i y peak was obse ed highe ups eam a s a ion 05 (Ma ínez
Agui e & Ga cía-León, 1991a).
Table 2 p esen s he U and Th con en s o he wa e s collec ed in he
Odiel i e , and he co esponding Th/U mass a io oge he wi h he
234U /238U, 23ºTh/234U and 228
Th/232
Th ac i i y a ios. In Fig. 3, U and Th
concen a ions along he i e channel a e shown. The Th/U a ios ound
a e consis en wi h he well known ac o highe end o Th o be
associa ed wi h he solid phase in i e s. On he o he hand, such esul s a e
highe han no mally encoun e ed in mos i e wa e s (Osmond &
I ano ich, 1992) sampled ups eam om he es ua y. These esul s,
howe e , a e qui e simila o he mass a ios ob ained o he es ua ine
wa e s o he Guadalqui i i e (Ma ínez-Agui e, 1991; Ma ínez
Agui e & Ga cía-León, 1992).
The 234U/238U ac i i y a ios epo ed in Table 2 a e unusually low o
a i e sys em. A weigh ed a e age o he da a o s a ions 02 o 07 is
1-07 ± 0-02. This alue is mo e ypical o a p ima y mine al ac i i y a io
om a e ilize manu ac u ing p ocess han he a e age disequilib ium
obse ed in i e s (Sco , 1982).
Sample 01 is clea ly a di e en case. I s low pH p omo es he dissolu ion
TABLE 2
U and Th Concen a ions (µg/1), Th/U Mass Ra io and Iso opic Ac i i y Ra ios in Wa e Samples Taken Along he Odie! Ri e
Sample [U] [Th] Th/U 214u¡21su210Th/214U21sTh/212Th
01 ¡5.9 ± 0·6 3·31±0·15 0·208 ± 0·012 1·60 ± 0,02 0· 157 ± 0·008 1·70 ± 0·07
02 2.75 ± 0·09 0· 145 ± 0·075 0,053 ± 0·027 1,06 ± 0,03 0•71 ± 0-21 4-51 ± 2-49
03 2-68 ± 0-16 0-447 ± 0-035 0-167 ± 0,017 1-07 ± 0-02 0-34 ± 0-03
04 4.39 ± 0-30 0-546 ± 0-059 0,134 ± 0-017 1-08±0-10 0-24 ± 0-02
os 4·28 ± 0-29 0-620 ± 0-061 0-151 ± 0-018 1-02 ± 0-09 0-37 ± 0-04 3-00 ± 0-25
06 10-7 ± 0-9 ¡ .¡7 ± 0-16 0-110 ± 0-018 1-04 ± 0-04 0-25 ± 0-03 1-87 ± 0-67
07 2-88 ± 0-07 0-450 ± 0-029 0-157±0,011 1-10 ± 0-02 0-29 ± 0-01 1-31±0-11
(a)
ú)
úJ
02 03 04 05 06 07
(b)
-a-
o
J
�
� ··�
01 02 03 04 05 06 C1l OT1
Fig. 3. U concen a ion (a) and Th concen a ion (b) in µg/1 in wa e samples along he
Odie! i e .
o U-iso ope ac i i ies om he solid phase o he i e sys em. In such
condi ions, he 234 U-iso ope is p e e en ially mobilized, esul ing in 234U
en ichmen in he aqueous phase ela i e o 238U (Gascoyne, 1982) and
hence he highe 234U /238U ac i i y a io obse ed in sample O l.
The 23ºTh/234U ac i i y a ios epo ed in Table 2 a e anomalously high
when compa ed wi h o he i e sys ems. Thus, ypical ac i i y a ios o
i e wa e s a e a ound Ü· l o less (Pla e e al., 1992; Ma ínez-Agui e &
Ga cía-León, 1992). In he p esen case he weigh ed a e age 23ºTh/234 U
(a)
T1 T2 T3 T4 Ts Ts
(b)
ID
ú)
o -·� j
T1 " .2 T3 T4 Ts Ts OT1 OT2
Fig. 4. U concen a ion (a) and Th concen a ion (b) in µg/1 in wa e samples along he
Tin o i e .
The ma e ial discha ged a s a ions 2 and 4 mus also con ain U. The ac
ha enhanced le els o U ha e no been obse ed is p obably ela ed o he
di e en ial mobili ies o Th and U in aqueous sys ems. The U being much
mo e mobile han Th, i will end o edis ibu e mo e apidly in he mass o
wa e along he i e channel, esul ing in a smoo he dis ibu ion pa e n,
compa ed o Th which will be inco po a ed o he solid pa icles e y as .
The iso ope ac i i y a ios p esen ed in Table 6 o s a ions 2 and 4 may
help o suppo his p oposi ion.

TABLE 6
U and Th Concen a ions (µg/1), Th/U Mass Ra ios and Iso opic Ac i i y Ra ios in Wa e Samples Along he Tin o Ri e
234u¡2Jsu 230Th/234U22sTh/232Th 230Th/232Th
Sample [U} [Th} Th/U
TI 9-26 ± 0-32 4-82 ± 0-23 0-521 ± 0-031 1-83 ± 0-03 0-25 ± 0-01 3-60 ± 0-12 2-67 ± 0-09
T2 3-20±0-15 11-8±3,6 3-69±1·13 1-07 ± 0-04 2-14 ±0-64 0-27 ± 0-05 1-90±0-21
T3 3-82 ± 0-18 0-193 ± 0-028 0-050 ± 0-006 1-09 ± 0-04 0-11±0-01 1-27 ± 0-22 7-2 ± 0-8
T4 3-87±0-19 5.33 ± 1-21 1-38 ± 0-32 1-11 ± 0-04 0-77±0-17 0-10 ± 0-03 1-90 ± 0-21
T5 3-42 ± 0-08 0-136 ± 0-024 0-040 ± 0-007 1-08 ± 0-02 0-085 ± 0-007 7.1 ±0·3
T6 3-68±0-12 0-155 ± 0-015 0·042 ± 0-004 1-08 ± 0-03 0-077 ± 0-004 1-09 ± 0-17 6-0 ± 0-6
OT1 3.97 ± 0-11 0-135 ± 0-016 0-034 ± 0-004 1-09 ± 0-02 0-060 ± 0-004 0-91 ± 0·18 5.9 ± 0-7
OT2 2-80 ± 0-16 0-021 ± 0-008 0-008 ± 0-003 1-11 ± 0-05 0-016 ± 0-002 7.4 ± 2-8
The weigh a e age o he 234U /238U ac i i y a io o 1-09 ± 0-02
( excluding sample Tl) is s a is ically iden ical o he weigh ed a e age
ob ained o he Odiel i e wa e samples. The e o e, simila conclusions
can be d awn on he o igin o U-iso ope signa u es. Howe e , he impac o
he p esence o he phosphogypsum piles on he Tin o i e wa e s wi h
espec o U-iso opes is no as high as ha o he di ec inpu o phospha e
e ilize p ocess was es on he Odiel i e . In ac , i is e y di icul o
iden i y he sou ces o U ac i i ies om he da a p esen ed in Table 6. I
any hing, he only i m conclusion is ha any Th-en ichmen a s a ions 2
and 4 is apidly emo ed om he aqueous column and p esumably
adso bed on o he solid pa icles su ace. In ac , all o he Th/U mass a ios
a e ,.._, 10�2, in good ag eemen wi h published da a o o he i e sys ems
(Sco , 1982; Ma ínez-Agui e, 1991).
The 23ºTh/234U ac i i y a ios a e consis en wi h he abo e a gumen s,
adding weigh o he conclusion ha discha ge o he Tin o i e om he
phosphogypsum piles con ains a g ea <leal mo e Th han U. The dec ease
in he 228Th/232Th ac i i y a io a s a ions 2 and 4 in he Tin o i e e lec s
he ela i e immobili y o 228Ra, a p ecu so o 228Tb in he decay se ies, in
he phosphogypsum piles.
Sedimen
The iso ope adioac i i y in bo om sedimen s in he Tin o i e a e gi en in
Table 7. I compa ed o published U da a o bo om sedimen s in o he
i e sys ems (Sco , 1982; Descamps & Foulquie , 1988; Mo ón e al.,
1988; Pla e e al., 1992) i becomes clea ha he i e bo om sedimen s
i e accumula ing U and i s daugh e s. The concen a ions o 238U, 234U,
226Ra and 23ºTh a e lowe han hose epo ed in Table 3 o he Odiel i e
bu signi ican ly highe han he published le els o undis u bed i e
sys ems, always below 60 mBq/g o all o hem (Sco , 1982; Ma ínez
Agui e , 1991; Ma ínez-Agui e & Ga cía-León, 1992; Pla e e al., 1992).
This is no he case o 232Tb and i s daugh e 228Tb, whe e he
concen a ions a e simila o hose ound in he li e a u e o unpe u bed
sys ems, usually below 57 mBq/g o 232Tb (Sco , 1982; Ma ínez-Agui e,
1991; Ma ínez-Agui e & Ga cía-León, 1992).
Howe e , he ac ha all U-de i ed ac i i ies inc ease owa ds he
con luence wi h he Odiel i e may e lec a possible ans e o adioac i e
ma e ial om he Odiel i e o he Tin o i e . The ways h ough which
his occu s should be in es iga ed, bu mus be ela ed mainly o he idal
cycle and suspended ma e dynamics.
The co esponding ac i i y a ios o he Tin o i e bo om sedimen s
a e p esen ed in Table 8. Again, as in he case o he Odiel i e , he
weigh ed a e age 234U /238U ac i i y a io o 1-04 ± 0-03 sugges s an
Sample
-
STl
ST2
ST3
ST4
ST5
ST6
SOT1
ND, No de ec ed.
TABLE 7
U- and Th-Iso ope and 226Ra Ac i i ies (mBq/g) in Sedimen Samples Taken Along he Tin o Ri e
23su231u226Ra232Th230Th
15,7 ± 1-3 16·8 ± 0,8 25·2 ± 0-9 11,5±3·0 20-3 ± 4-0
195·2 ± 4-4 198-5 ± 4.5 146-0 ± 2-7 30·8 ± ¡.o 341,7±11·6
74.5 ± 2-8 80-9 ± 3.0 33.2 ± 0-5 45·0 ± 4.0 66·4 ± 5-2
133.1 ± 3,8 137,8 ± 3.9 49,6±1·1 36-1 ± 3·6 88-6 ± 6-6
342·0 ± 7.5 363·8 ± 7.9 46·1 ± ¡.o 25,3 ± 2·0 231-0 ± 12·3
516·9 ± 15-9 531-2± 16·3 149-9 ± 0-8 47.5 ± 4-0 490,8 ± 23·3
299-0 ± 12-6 304-5 ± 12-8 50-3±1·7 53-7±4·1 279·5 ± ¡5.¡
22sTh
ND
34.3 ± 1-5
48,9 ± 4-8
36-3 ± 4,1
30-8 ± 2·3
41·0 ± 4·0
55.4 ± 4.0
TABLE 8
U and Th Concen a ions (µg/g), Th/U Mass Ra io and Iso opic Ac i i y Ra ios in Sedimen Samples Along he Tin o Ri e
Sample [U][ThjTh/U
STI 1·26 ± 0·06 2·84 ± 0-74 2·24 ± 0.59
ST2 15·7 ± 0-5 7-6±0-3 0-485 ± 0·023
ST3 6-0 ±0·2 11-1 ± l·O 1·85±0·18
ST4 10-7 ± 0·3 3.9 ± 0-9 0·831 ± 0-087
ST5 27-5 ± 0·6 6-2 ± 0·5 0,226 ± 0,019
ST6 41-6±1·3 11,7 ± 1-0 0-282 ± 0·025
SOT1 24-0 ± l·O 13·2± l·O 0,550 ± 0-048
234U/23su 230Th/234U
1,07 ± 0-07 1-21±0·25
1.02 ± 0,02 1-72 ± 0·07
1·09 ± 0·05 0·82 ± 0-07
1·04 ± 0,03 0,64 ± 0·05
1-06 ± 0-02 0·64 ± 0·04
1·03 ± 0,02 0-92 ± 0·05
1-02 ± 0·03 0·92 ± 0·06
226
Ra/230Th
1-24 ± 0,25
0-43 ± 0·02
0·50 ± 0,04
0,56 ± 0,04
0,20 ± 0,01
0·31 ± 0·02
0·18±0,01
22sTh/232Th 230Th/232Th
1-77 ± 0-56
1·11 ± 0-05 11·1 ±0·5
1-09 ± 0-13 1-48
± 0· 15
1-01 ± 0,14 2-46 ± 0·26
1-22±0·10 9.2 ± 0·6
0,86 ± 0-10 10·3 ± 0·8
1-04 ± 0-09 5·2 ± 0·3
a i icial ongm o U-iso ope signa u es such as phosphogypsum piles
si ua ed along i s igh bank.
The gene al end in he iso opic a ios sugges a U-en ichmen in he
Tin o i e bo om sedimen s. Obse a ions made om he sedimen s in he
Odiel i e a e also alid o he Tin o i e case.
CONCLUSIONS
A ca e ul sampling campaign ca ied ou in 1989 o i e wa e and
bo om sedimen samples along he Odiel and Tin o i e s (sou hwes
Spain) has yielded comp ehensi e U, Th and 226Ra iso opic da a. These
da a ha e been in e p e ed o es ablish he connec ion be ween he
obse ed anomalously high concen a ions o U-, Th- and 226Ra-iso opes
in wa e s and sedimen s, and he ope a ions o phospha e e ilize ac o ies
loca ed in a zone i ually su ounded by bo h i e s. The conclusion based
on he iso opic da a is ha bo h liquid and solid was es a ising om he
e ilize p oduc ion, and discha ged om his indus ial zone, a e
esponsible o he obse ed adioac i i y enhancemen in he immedia e
en i onmen o he e ilize plan s.
ACKNOWLEDGEMENTS
The au ho s hank he Spanish DGICYT (con ac PB89-0621) and he
AMA o Jun a de Andalucía o he inancial suppo o his wo k. They
also wish o hank J. M. Ab il, G. Manjón and J. Díaz o helping in he
sampling, and a e obliged o Miss Sand a Hasle o Iso ope Geoscience
Sec ion, Ha well Labo a o y o in aluable help wi h he analy ical wo k.
REFERENCES
Bae slé, L. H. (1991) S udy o he adionuclides con ained in was es p oduced by
he phospha e indus y and hei impac on he en i onmen . Commission o
he Eu opean Communi ies, EUR 13262 EN, Nuclea Science and
Technology.
Bo ego-Flo es, J. & Pendón-Ma ín, J. C. (1988). Algunos ejemplos de in luencia
de los p ocesos an ópicos en el medio sedimen a io: La Ría de Huel a.
Hena es, Re . Geol., 2, 299-305 (in Spanish).
Descamps, B. & Foulquie , L. (1988). Na u al adioac i i y in he p incipal
cons i uen s o F ench i e ecosys ems. Radia ion P o ec ion Dosime y,
24(1), 143----47.

Gascoyne, M. (1982). Geochemis y o he Ac inides and hei daugh e s. In
U anium Se ies Disequilib ium: Applica ions o En i onmen al P oblems, ed.
I ano ich, M. & Ha mon, R. S. Cla endon P ess, Ox o d, chap. 2.
Gascoyne, M. (1992). Geochemis y o he Ac inides and hei daugh e s. In
U anium Se ies Disequilib ium: Applica ions o Ea h, Ma ine and En i on
men al Sciences, ed. I ano ich, M. & Ha mon, R. S. Cla endon P ess,
Ox o d, chap. 2.
Guimond, R. J. & Ha din, J. M. (1989). Radioac i i y eleased om phospha e
con aining e ilize s and om gypsum. Radia . Phys. Chem., 34, 309-15.
I ano ich, M. & Mu ay, A. (1992). U anium Se ies Disequilib ium: Applica ions
o Ea h, Ma ine and En i onmen al Sciences, ed. I ano ich, M. & Ha mon,
R. S. Cla endon P ess, Ox o d, chap. 5.
Kos e , H. W., Ma wi z, P. A., Be ge , G. W., an Wee s, A. W., Hegel, P. &
Nienwenh ize, J. (1991). 210Po, 210Pb, 226Ra in aqua ic ecosys ems and
polde s, an h opogenic sou ces, dis ibu ion and enhanced adia ion doses in
he Ne he lands. In V In . Symp. on he Na ional Radia ion En i onmen ,
Salzbu g, Aus ia.
Lally, A. E. & Eakins, J. D. (1978). Pape p esen ed a Symp. De e . Radionuclides
En i on. Bio. Ma s. CEGB, London.
Ma ínez-Agui e, A. (1991 ). Radioac i idad na u al en di e sos compa imen os
na u ales de Andalucía. PhD hesis, Se ille Uni e si y, Spain (in Spanish).
Ma ínez-Agui e, A. & Ga cía-León, M. (1991a). Na u al adioac i i y enhance
men by human ac i i ies in i e s o sou hwes o Spain. J. Radioanal. Nucl.
Chem., Le e s, 155(2), 97-105.
Ma ínez-Agui e, A. & Ga cía-León, M. (1991b). U- and Ra-iso opes in he
Guadalqui i i e , sou h o Spain. In V ln e na ional Symposium on he
Na u al Radia ion En i onmen , Salzbu g, Aus ia.
Ma ínez-Agui e, A. & Ga cía-León, M. (1992). Na u al adioac i i y in he
Guadalqui i i e , sou h o Spain (submi ed).
Miyake, Y., Sugimu a, Y. & Tsubo a, H. (1964). Con en o U, Ra, and Th in i e
wa e s in Japan. In The Na u al Radia ion En i onmen , eds. Adams, J. &
Lowde , W. M . . Uni e si y o Chicago P ess, Chicago, IL, pp. 219-25.
Miyake, Y., Sugimu a, Y. & Yasujima, T. (1972). Tho ium iso ope con en in i e
wa e in Japan. Pape s in Me eo ology and Geophysics, 24(1), 67-73.
Moo e, W. S. (1967). Amazon and Mississippi i e concen a ions o u anium,
ho ium and adium iso opes. Ea h Plane . Sci. Le ., 2, 231-4.
Mo ón, M.C., Ma ínez-Agui e, A. & Ga cía-León, M. (1988). De e mina ion o
le els o U, Th and Po om di e en en i onmen al samples. In In e na ional
Con e ence on En i onmen al Radioac i i y in he Medi e anean A ea. SNE
ENS, Ba celona, Spain, p. 111.
Osmond, J. K. & I ano ich, M. (1992). U anium se ies mobilisa ion and su ace
hyd ology. In U anium Se ies Disequilib ium: Applica ions o Ea h, Ma ine
and En i onmen al Sciences, ed. I ano ich, M. & Ha mon, R. S. Cla endon
P ess, Ox o d, chap. 8.
Paul, A., Londhe, V. & Pillai, K. (1980). 228Ra and 226Ra le els in a i e
en i onmen and i s modi ica ion by human ac i i ies. In Na u al Radia ion
En i onmen III, Vol. 2. US Depa men o Ene gy, pp. 1633-54.
Pla e , A. J., I ano ich, M. & Dugdale, R.E. (1992). U anium se ies disequili
b ium in i e sedimen s and wa e s: he signi icance o anomalous ac i i y
a ios. Appl. Geochem., 7(2), 1-5.
San schi, P., Li, Y. H. & Bell, J. (1979). Na u al adionuclides in he wa e o
Na aganse Bay. Ea h Plane . Sci. Le ., 45, 201-13.
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, ed.
l ano ich, M. & Ha mon, R. S. Cla endon P ess, Ox o d, chap. 8.
S ain, C. D. (1979). An e alua ion o adium-226 and adon-222 concen a ions
in g ound and su ace wa e s nea phospha e mining and manu ac u ing
acili y. Pape p esen ed a Annual Mee ing o he Heal h Physics Socie y,
Philadelphia, PA.
UNSCEAR (1977). Ionizing Radia ion and Biological E ec s. Uni ed Na ions
Scien . Comm. on E ec o A omic Radia ion, New Yo k, pp. 86-91.
Van de Heidje, H., Klijn, P. & Passchie , W. (1988). Radiological impac s o he
disposal o phosphogypsum. Radia ion P o ec ion Dosime y 24(1), 419-23.