A particle-tracking method for simulating the dispersion of non-conservative radionuclides in coastal waters
Abstract
A particle-tracking method has been used to simulate the dispersion of non-conservative radionuclides in the sea. Three dimensional turbulent diffusion and the interactions between water, suspended matter and bottom sediments are simulated using a stochastic method. Kinetic transfer coefficients, as in finite difference models, are used to describe the transfers between the liquid and solid phases. Deposition of suspended matter and erosion of sediment are also included in the model. The method has been applied to simulate the dispersion of 137Cs and 239,240Pu in the English Channel and the results have been compared with those of a finite difference model. The results from both techniques are, in general, in good agreement.
Full text
a
A pa icle- ackingme hod o simula ing he
dispe sion o non-conse a i e adionuclides in
coas al wa e s
R. Pe i!aa*nnez
a,
*, A.J. Ellio
b
Depa amen o Fı´sica Aplicada I, Uni e si y o Se illa, EU Ingenie ı´aTe
´cnica Ag ı´cola, C a. U e a km 1,
41013 Se illa, Spain
b
Cen e o Applied Oceanog aphy, Uni e si y o Wales, Bango , Ma ine Science Labo a o ies,
Menai B idge, Anglesey LL59 5EY, UK
Abs ac
A pa icle- acking me hod has been used o simula e he dispe sion o non-conse a i e
adionuclides in he sea. Th ee dimensional u bulen diffusion and he in e ac ions be ween
wa e , suspended ma e and bo om sedimen s a e simula ed using a s ochas ic me hod.
Kine ic ans e coefficien s, as in fini e diffe ence models, a e used o desc ibe he ans e s
be ween he liquid and solid phases. Deposi ion o suspended ma e and e osion o sedimen
a e also included in he model. The me hod has been applied o simula e he dispe sion o
137
Cs and
239,240
Pu in he English Channel and he esul s ha e been compa ed wi h hose o a
fini e diffe ence model. The esul s om bo h echniques a e, in gene al, in good ag eemen .
Keywo ds: Model; Dispe sion; Pa icle- acking; Fini e diffe ence; Radionuclides; English Channel
1. In oduc ion
The s a e-o - he-a models used o simula e he dispe sion o adioac i i y in he
sea consis o fini e elemen s o , mainly, fini e diffe ence models ha sol e he
hyd odynamic equa ions oge he wi h he ad ec ion–diffusion dispe sion equa ion,
in ei he a wo dimensional o a h ee dimensional o m (Ha ms, 1997; Pe i!
aa*
nnez &
*Co esponding au ho . Tel.: +34-95-4233669; ax: +34-95-4232644.
E-mail add esses: [email p o ec ed] (R. Pe i!
aa*
nnez), [email p o ec ed] (A.J. Ellio )
Regue a, 1999). I he model is applied o simula e he dispe sion o non-
conse a i e adionuclides, hen he in e ac ions wi h he solid phases (suspended
ma e and bo om sedimen s) mus also be conside ed. This implies ha he
suspended ma e equa ion, including he se ling o pa icles, deposi ion and e osion
o he sedimen , mus be sol ed oo (Ald idge, 1998; Ma g elash ily, Made ich, &
Zheleznyak, 1997; Piasecki, 1998; Pe i!
aa*
nnez, 1999, 2000). Abso p ion/deso p ion
eac ions a e usually desc ibed using kine ic ans e coefficien s ins ead o he less
app op ia e equilib ium dis ibu ion coefficien s, kd. These models a e compu a-
ionally expensi e due o he ac ha a la ge numbe o equa ions mus be sol ed.
Also, since fini e diffe ence models wo k wi h adionuclide concen a ions, he whole
compu a ional g id mus be swep each ime s ep. Finally, he CFL condi ion
(Kowalick & Mu y, 1993) limi s he size o he ime s ep ha can be used i an
explici scheme is used o sol e he hyd odynamic equa ions. In consequence, la ge
CPU imes may be equi ed e en using ecen supe compu e s (Pe i!
aa*
nnez, 1999).
An al e na i e app oach is o make use o pa icle- acking echniques. In his
kind o model, he impac o he CFL c i e ion can be educed by making he
hyd odynamic compu a ions off-line. Also, ad ec ion can be simula ed o a high
deg ee o accu acy since nume ical dispe sion (which appea s when he ad ec ion
equa ion is sol ed wi h fini e diffe ences) is no in oduced. Pa icle- acking models
ha e al eady been used o simula e he dispe sion o conse a i e ace s and oils
spills (Hun e , 1987; Ellio , Dale, & P oc o , 1992; P oc o , Ellio , & Fla he ,
1994a, b). In such applica ions, a elease o adioac i i y o he sea is modelled as a
numbe o disc e e pa icles, each pa icle being equi alen o a numbe o uni s (Bq,
moles, a oms, e c.). Then he pa h ollowed by each indi idual pa icle is compu ed,
u bulen diffusion being modelled as a h ee dimensional andom walk (Mon e
Ca lo) p ocess. The densi y o pa icles is calcula ed o ob ain he adioac i i y
concen a ions a he end o he simula ion. The main difficul y ha appea s in he
simula ion o he dispe sion o non-conse a i e adionuclides is he ea men o
abso p ion and deso p ion: how o decide i each pa icle is fixed o suspended
ma e o bo om sedimen s (i ini ially dissol ed) o i i is edissol ed (i ini ially
p esen in he suspended ma e o he bo om sedimen ). The main con ibu ion o
his pape consis s o a new me hod de eloped o sol e his p oblem: a o mula ion
(sui able o a pa icle- acking model) o desc ibe he ans e s o adionuclides
be ween wa e , suspended ma e and bo om sedimen s, based upon kine ic ans e
coefficien s and a s ochas ic me hod, is p esen ed. I is impo an o poin ou ha
exac ly he same physical pa ame e s as in he equi alen fini e diffe ence models a e
used.
The pa icle- acking modelling echnique is well sui ed o p oblems in which high
con aminan g adien s a e in ol ed, since nume ical diffusion is no in oduced.
This, oge he wi h he ac ha i can gi e e y as answe s, e en in a PC, allows he
echnique o be conside ed as a e y use ul p edic i e ool in he assessmen o
con amina ion ollowing acciden al o delibe a e eleases o adionuclides.
The pa icle- acking model is p esen ed in he nex sec ion, hen an applica ion o
he English Channel is shown. The model has been used o simula e he dispe sion o
an ins an aneous hypo he ical elease o adionuclides om La Hague nuclea uel
ep ocessing plan , loca ed on he F ench sho e o he English Channel. Simula ions
ha e been ca ied ou o wo adionuclides wi h e y diffe en geochemical
beha iou s: he ela i ely conse a i e
137
Cs and he high eac i e
239,240
Pu. A fini e
diffe ence model o he Channel has been p e iously de eloped and alida ed
h ough he s udy o he dispe sion o hese adionuclides, compa ing obse ed and
compu ed concen a ions in wa e , suspended ma e and bo om sedimen s
(Pe i!
aa*
nnez and Regue a 1999; Pe i!
aa*
nnez, 2000). Thus esul s o he pa icle- acking
model will be compa ed wi h he ou pu o he fini e diffe ence model in equi alen
simula ions and he ela i e ad an ages o each echnique will be assessed.
2. The pa icle- acking model
2.1. Ad ec i e anspo
The posi ion ec o o a gi en pa icle, þD ðÞ, a ime þD is compu ed om
þD ðÞ ðÞ
D ¼q ðÞ;ð1Þ
whe e D is he ime s ep used in he model and q he cu en ec o o componen s u
and along he xand yaxes, espec i ely. Cu en s a e ob ained by unning a
hyd odynamic model in ad ance. S anda d idal analysis is used o de e mine he
idal cons an s ( ide ampli ude and phase) o each g id cell o he hyd odynamic
model. These cons an s a e e alua ed o bo h componen s o he flow and can be
de i ed o as many idal cons i uen s as desi ed. In his wo k, only he wo main
semidiu nal ides, M2and S2, will be conside ed. Once he idal cons an s a e known,
compu a ion o he flow ec o , q, jus in ol es he calcula ion and addi ion o a ew
cosine e ms. As a consequence, he e alua ion o he idal ad ec i e anspo o
pa icles is e y as and is no limi ed by he CFL c i e ion.
Fo eal applica ions, fi s o de accu acy in he pa icle- acking scheme is
adequa e. In simula ions o he mo emen o d ogues in an es ua ine en i onmen ,
Ellio and Cla ke (1998) ound no imp o emen in he esul s when a second o de
accu acy scheme was used o simula e he mo emen o su ace d i e s by he
pa icle- acking echnique. Mo eo e , in ocean dispe sion p oblems, he effec s o
u bulence will mask any small e o s in he ad ec ion scheme.
The ne esidual cu en in he modelled a ea mus be added o qsince a esidual
anspo canno be gene a ed wi h he pu e ha monic idal cu en s ha a e used in
pa icle- acking calcula ions. The esidual flow ec o s can also be ob ained om
he (p e iously un) hyd odynamic model. Wind-induced anspo can be included
in he model by assuming ha he su ace wind-induced cu en is a pe cen age o
he wind speed, gene ally 2–3% (P oc o e al., 1994b). This cu en dec eases
loga i hmically below a dep h z1( he hickness o he wind-d i en su ace laye ) o
ze o a a dep h z2. Eckman heo y (Pugh, 1987) p edic s ha he su ace wind-
induced cu en due o a s eady wind blowing o e deep wa e should be deflec ed o
he igh o he wind di ec ion (in he no he n hemisphe e). Howe e , obse a ional
e idence sugges s ha his deflec ion angle can be neglec ed (P oc o e al., 1994b) in
shallow coas al wa e s.
2.2. Tu bulen diffusion
Th ee dimensional diffusion is simula ed using a andom walk me hod. I has been
shown (P oc o e al., 1994b; Hun e , 1987) ha i is a simula o o Fickian diffusion
p o ided ha he maximum size o he ho izon al s ep gi en by he pa icle, Dh,is
Dh¼ffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffi
12KhD
pð2Þ
in he di ec ion 2pRAN, whe e RAN is a andom numbe be ween 0 and 1. This
equa ion gi es he maximum size o he s ep. In p ac ice, i is mul iplied by RAN o
ob ain he eal size a a gi en ime and o a gi en pa icle. Simila ly, he size o he
e ical s ep is
D ¼ffiffiffiffiffiffiffiffiffiffiffiffiffi
2K D
pð3Þ
gi en ei he owa ds he sea su ace o he sea bo om. Khand K a e he ho izon al
and e ical diffusion coefficien s, espec i ely.
2.3. Radioac i e decay
Conside he adioac i e decay equa ion:
qC
q ¼lC;ð4Þ
whe e lis he adioac i e decay cons an . This equa ion can be ea ed using a
s ochas ic me hod i i is assumed ha he p obabili y po emo al o a pa icle a
each ime s ep is (Hun e , 1987; P oc o e al., 1994b)
p¼1elD :ð5Þ
In p ac ice, a andom numbe is gene a ed o each pa icle on each ime s ep. I
RAN4p hen he pa icle is emo ed om he compu a ion.
2.4. T ans e s be ween wa e , suspended ma e and bo om sedimen s
Conside a wo phase sys em. I he ans e s o adionuclides be ween he wo
phases a e desc ibed h ough he kine ic ans e coefficien s k1and k2, he equa ions
ha gi e he ime e olu ion o ac i i y in he wo phases a e
qA1
q ¼k1A1þk2A2;ð6Þ
qA2
q ¼k1A1k2A2:
These equa ions a e easily sol ed using fini e diffe ences. In pa icle acking, a label
is gi en o each pa icle o diffe en ia e i i is in phase l o 2. I he pa icle is in phase
1, he p obabili y p1 ha he pa icle goes o phase 2 in each ime s ep is
p1¼1ek1D :ð7Þ
Simila ly, i he pa icle is in phase 2, he p obabili y p2 ha i goes o phase 1 each
ime s ep is
p2¼1ek2D :ð8Þ
Thus, in pa icle acking, he exchanges be ween wo phases can be modelled as wo
decay p ocesses wi h p obabili ies p1and p2. These p ocesses a e ea ed as he
adioac i e decay p ocess desc ibed abo e. I a gi en pa icle goes om one phase o
he o he , i s label is changed and he new co esponding decay p ocess is conside ed
a he nex ime s ep.
This me hod has been compa ed wi h he fini e diffe ence solu ion o he sys em o
Eq. (6). I has been conside ed ha all adionuclides a e, a ¼0, in phase 1. Thus,
he solu ion gi en by each me hod e e s o he pe cen ages o adionuclides ha a e
in phase 1 a each ollowing ime s ep. Resul s ob ained by bo h me hods a e
p esen ed in Fig. 1, using 200 and 10,000 pa icles in he s ochas ic simula ion. High
fluc ua ions occu wi h 200 pa icles, bu he fini e diffe ence solu ion is well
modelled i 10,000 pa icles a e used in he pa icle- acking calcula ion. The mean
alue and s anda d de ia ion o he diffe ence be ween fini e diffe ence and
s ochas ic solu ions a e p esen ed in Table 1 o diffe en numbe s o pa icles in
Fig. 1. Time e olu ion o he pe cen age o adionuclides in phase 1 gi en by he solu ion o he
diffe en ial equa ions using fini e diffe ences and he pa icle- acking me hod, wi h 200 and 10,000
pa icles.
he s ochas ic me hod. I can be seen ha bo h he mean alue and s anda d
de ia ion o he diffe ence dec ease as he numbe o pa icles conside ed in he
s ochas ic simula ion inc eases. Accep able esul s a e ob ained o numbe s o
pa icles o he o de o 10,000.
The s ochas ic me hod can be ex ended o he case in which he e a e h ee
diffe en phases: wa e , suspended ma e and ac i e bo om sedimen s (pa icles
wi h a diame e 562.4 mm). I is conside ed ha he ans e o adionuclides om
he solid phases o wa e is go e ned by a kine ic ans e coefficien k2, he ans e
om wa e o suspended ma e by k1m and he ans e om wa e o he sedimen
by k1s. The abso p ion o adionuclides depends on he su ace o pa icles pe wa e
olume uni . Thus he exchange su ace and exchange eloci y concep s ha e been
used (Pe i!
aa*
nnez, Ab il, & Ga c!
ııa-Le!
oon, 1996; Pe i!
aa*
nnez & Ma !
ıınez-Agui e, 1997;
Pe i!
aa*
nnez, 1999, 2000). Following hese pape s:
k1m ¼w1
3m
R;ð9Þ
k1s ¼w1
3L
RH ;ð10Þ
whe e w1is he exchange eloci y, mis he suspended ma e concen a ion, and R
a e he densi y and mean adius o suspended ma e pa icles, Lis he a e age
mixing dep h ( he dis ance o which he dissol ed phase pene a es he sedimen ),
is a co ec ion ac o ha akes in o accoun ha no all he mass o he sedimen is
in con ac wi h wa e and Hgi es he hickness o he wa e laye abo e he sea
bo om ha in e ac s wi h he sedimen . In a wo dimensional dep h-a e aged
model, His equal o he wa e dep h. Since pa icle acking is h ee dimensional, H
is le as a ee pa ame e o be calib a ed.
The decay equa ions ha a e equi alen o he diffe en ial equa ions ha desc ibe
ans e s be ween he h ee phases, p esen ed o ins ance in Pe i!
aa*
nnez (2000), a e
qCd
q ¼k1mCdk1sCd;ð11Þ
Table 1
Mean alue and s anda d de ia ion o he diffe ence be ween he pe cen age o adionuclides in phase 1
gi en by fini e diffe ences and he s ochas ic me hod
a
NP hDis
100 0.654 2.861
200 0.637 2.220
500 0.296 1.557
1000 0.335 1.021
10,000 1.56 10
2
0.309
100,000 6.17 10
2
0.114
a
NP is he numbe o pa icles used in he simula ion.
qCs
q ¼k2Cs;ð12Þ
qAs
q ¼k2 As:ð13Þ
whe e Cd,Csand Asa e adionuclide concen a ions in wa e , suspended ma e and
ac i e bo om sedimen s, espec i ely. A label is gi en o each pa icle o classi y in
which phase i is p esen . Depending on he label o he pa icle, he co esponding
decay equa ion is ea ed. I he pa icle is in suspended ma e , he p obabili y ha i
goes o he dissol ed phase, in each ime s ep, is
p¼1ek2D :ð14Þ
Simila ly, i he pa icle is in he bo om sedimen , he p obabili y ha i is
edissol ed is
p¼1ek2 D :ð15Þ
I he pa icle is ini ially dissol ed and i s dis ance o he sea bo om is smalle han
H, i can go o any o he wo solid phases wi h a p obabili y
p¼1ek1mþk1s
ðÞD :ð16Þ
A andom numbe is gene a ed o decide i he pa icle is effec i ely emo ed om
solu ion. I i is, he no malized p obabili y ha he pa icle goes o he sedimen is
calcula ed as
p¼ps
pmþps
;ð17Þ
whe e
pm¼1ek1mD ;ð18Þ
ps¼1ek1sD :ð19Þ
A second andom numbe is hen gene a ed. I RAN5p, hen he pa icle goes o
he sedimen . I RAN >p, hen i goes o he suspended ma e . O cou se, i he
dis ance o he pa icle o he sea bo om is la ge han H, only he decay o
suspended ma e is conside ed since such pa icles canno in e ac wi h he
sedimen .
A nume ical expe imen has been ca ied ou o es he me hod in which a olume
o wa e wi h a gi en suspended ma e concen a ion and ac i e sedimen on he
bo om is conside ed. A dissol ed adioac i e ace is added and he equa ions ha
gi e he ime e olu ion o ac i i ies in he h ee phases a e sol ed using fini e
diffe ences and he s ochas ic me hod. The ollowing ealis ic pa ame e s ha e been
used: w1¼2:1108m/s, k2¼1:2105s
1
,m¼10 ppm, R¼15 mm,
¼2600 kg/m
3
,L¼0:01 m, ¼1, ¼0:1, H¼0:2 m wi h 10,000 pa icles being
used in he pa icle- acking simula ion. The compa ison be ween bo h me hods is
p esen ed in Fig. 2, whe e he ime e olu ion o he ac ion o ace ha is
dissol ed, in suspended ma e and in he sedimen is p esen ed. The simula ion
shows ha he s ochas ic me hod solu ion is in e y good ag eemen wi h he fini e
diffe ence solu ion o he h ee phases. Indeed, solu ions co esponding o bo h
me hods canno be dis inguished in he case o wa e and sedimen .
2.5. Suspended ma e deposi ion and sedimen e osion
The suspended ma e concen a ions o e he model domain can be ob ained by
unning in ad ance a fini e diffe ence suspended ma e model. Resul s a e hen
analyzed in a simila way o cu en s, so ha he suspended ma e concen a ion a
each poin and o any ime can be ob ained as he simple calcula ion o cosine
unc ions.
Suspended ma e alls o he sea bo om wi h a se ling eloci y ws. I a pa icle (in
he pa icle- acking sense, no a suspended ma e pa icle) is fixed o suspended
ma e , i s posi ion abo e he bo om, z, a ime þD is ob ained om
z þD ðÞz ðÞ
D ¼ws:ð20Þ
I z þD ðÞ40, hen he pa icle is conside ed o fix o he sedimen and i s label is
app op ia ely changed.
A s anda d o mula o floccula ion has been used o ep esen he inc ease in he
se ling eloci y as he suspended ma e concen a ion inc eases (Cla ke & Ellio ,
1998; Eisma, 1993; Pe i!
aa*
nnez, 2000)
ws¼a1ma2;ð21Þ
whe e a1and a2a e ob ained om measu emen s o om model calib a ion. The
pa icle- acking model is h ee dimensional. I he fini e diffe ence suspended ma e
model is dep h-a e aged, i s ou pu is he dep h-a e aged suspended ma e
concen a ion. A Rouse p ofile is hen used o esol e he e ical s uc u e o
suspended ma e . This allows he calcula ion o he suspended ma e concen a ion
a heigh zabo e he bo om, mz, om he dep h-a e aged suspended ma e
concen a ion m(Cla ke & Ellio , 1998):
mz¼m1ws=bku*
h
z
ws=bku *;ð22Þ
whe e his wa e dep h, kis he on Ka man cons an (0.4), bis an a bi a y cons an
usually aken as 1 (Eisma, 1993; Cla ke & Ellio , 1998) and u*is he scala ic ion
eloci y
u*¼kq
jj
ln h=z0
1;ð23Þ
whe e z0is he bo om oughness. The co esponding alue o mzis used o calcula e
k1m a he posi ion o each pa icle om Eq. (9).
E osion o he sedimen has been desc ibed in e ms o he e osion cons an
concep (Nicholson & O’Conno , 1986). Thus, he p obabili y ha a pa icle is
emo ed om he sedimen and inco po a ed o he wa e column as suspended
ma e is
p¼1eE jqjMD ;ð24Þ
whe e Eis he e osion cons an and Mis some powe o he wa e eloci y ypically
in he ange 2–5 (P andle, 1997). Thus, he e osion desc ip ion used in p e ious fini e
diffe ence models (Pe i!
aa*
nnez, 1999, 2000) has been con e ed in o a s ochas ic o m. I
is conside ed ha e osion can only ake place i he wa e eloci y is la ge han a
Fig. 2. Time e olu ion o he ac ion o adionuclides in wa e , suspended ma e and bo om sedimen s
gi en by fini e diffe ences and by he pa icle- acking me hod wi h 10,000 pa icles. Solid lines co espond
o he s ochas ic solu ion and dashed lines o he fini e diffe ence solu ion.
3.2. Discussion
Pa icle acking is a powe ul ool ha can be applied in he assessmen o
adioac i e con amina ion ollowing an acciden al elease in aqua ic en i onmen s in
gene al. Also, he me hod can be applied o bo h conse a i e and non-conse a i e
adionuclides, using he same concep ual app oach o he in e ac ions be ween
Fig. 6 (con inued).
Fig. 7.
239,240
Pu ac i i y concen a ions in wa e (mBq/l), suspended ma e (Bq/g) and ac i e sedimen
(Bq/g) gi en by he fini e diffe ence (a) and he pa icle- acking (b) models.
liquid and solid phases as used in fini e diffe ence models. The pa icle- acking
echnique, combined wi h idal analysis and mean flow da abases o he
hyd odynamics, p esen s wo clea ad an ages o e fini e diffe ences: speed o
Fig. 7 (con inued).
compu a ion and he ac ha i does no in oduce nume ical diffusion. The numbe
o pa icles used in simula ions depends on he speed o compu a ion and/o he
accu acy equi ed. Fo example, P oc o e al. (1994b) used 4000 pa icles o
simula e an oil spill du ing eal- ime o ecas ing o an inciden in he A abian Gul .
Howe e , i is possible ha , due o he geochemical beha iou o ce ain
adionuclides, he ac i i y concen a ions in some o he phases may no be
esol ed. This is he case o
137
Cs in suspended ma e . The numbe o pa icles used
in he simula ion should be o he o de o 10
6
o be able o calcula e, wi h
easonable accu acy, ac i i y concen a ions in suspended ma e bu hen he
compu ing ime would be simila o ha o he fini e diffe ence model. Howe e , i
we a e in e es ed in he assessmen o con amina ion ollowing an acciden , i is
p obably enough o calcula e ac i i ies in wa e and bo om sedimen s, which a e he
phases whe e almos all he adioac i i y is p esen . I he mos impo an aspec is
he speed o compu a ion, he numbe o pa icles can be educed. Fo ins ance, i
137
Cs dispe sion is simula ed using 20,000 pa icles, good esul s a e s ill ob ained in
wa e and bo om sedimen s and he compu a ion ime is educed o 2.6% o ha
equi ed by he fini e diffe ence model. In he case o
239,240
Pu, he numbe o
pa icles could be educed mo e and ac i i ies in he h ee phases may s ill be
calcula ed since Pu is mo e widely dis ibu ed be ween he h ee phases han Cs.
The pa icle- acking me hod is ully 3-D and akes accoun o ho izon al
ad ec ion plus u bulen diffusion in he x–y–zdi ec ions. In he p esen applica ion,
he idal and esidual flows ha e been compu ed by a dep h-a e aged 2-D
hyd odynamic model. A 2-D hyd odynamical model is adequa e due o he e y
s ong idal cu en s and he e ically well-mixed cha ac e o he coas al wa e s.
Howe e , he pa icle- acking me hod is sui able o use wi h a 3-D hyd odynamic
model (e.g. Ha ms, Ka che , & De hleff, 2000) and he manne in which e ical
s abili y can inhibi e ical mixing can be pa ame e ised in such applica ions by
making he e ical s ep-size a unc ion o he s abili y o he wa e column.
4. Conclusions
The pu pose o his pape is o demons a e he iabili y o new pa icle- acking
algo i hms o he simula ion o p ocesses ha in ol e chemical specia ion. The
pa icle- acking me hod is commonly used o oil and chemical spill applica ions
whe e he e is a need o apid esponse simula ions. In such applica ions, a
significan inc ease in compu a ional speed is achie ed by compu ing he
hyd odynamics ‘off-line’ and hen using idal p edic ion and mean flow da abases
o econs uc he wa e mo emen . This a oids he CFL c i e ion du ing he apid
esponse applica ion, al hough he pa icle- acking ime-s ep mus be kep
easonably sho in o de o main ain he accu acy o he fi s o de ad ec ion
scheme ha is used o compu e he pa icle mo emen . While i would also be
easible o sol e fini e diffe ence specia ion equa ions using a p e-compu ed flow
field, he p oposed echnique has he ad an age ha he compu a ional ime will be
e y sho i a ela i ely small numbe o pa icles is used in he simula ion.
Mo eo e , he me hod will be mo e efficien i he con aminan pa ch co e s only a
small ac ion o he g id domain (Hun e , 1987) and he accu acy o he esul s can
be imp o ed by eleasing la ge numbe s o pa icles}al hough a he expense o an
inc eased simula ion ime. One o he main ad an ages o he pa icle- acking
me hod is he ad-hoc manne in which pa icle cha ac e is ics can be defined. Fo
example, non-Fickian dispe sion can be eadily simula ed by a aching an age o
each pa icle (equal o he ime since he elease o he pa icle in o he compu a ion)
and hen making he diffusi e s ep o he pa icle a unc ion o i s diffusion ime.
In he new model, he in e ac ions be ween he liquid and solid (suspended ma e
and bo om sedimen ) phases ha e been desc ibed in e ms o kine ic ans e
coefficien s, as in ac ual fini e diffe ence models. A s ochas ic me hod has been
de eloped o simula e such in e ac ions. Deposi ion o pa icles and e osion o he
sedimen a e also included in he model. A Rouse p ofile is also used o es ima e he
e ical s uc u e o suspended ma e concen a ions. As a demons a ion o he
me hod, he pa icle- acking model has been used o simula e he dispe sion o
adionuclides in he English Channel. A fini e diffe ence model was p e iously
de eloped and alida ed o he Channel. Thus he ou pu om bo h models has
been compa ed. Two adionuclides wi h diffe en geochemical beha iou s,
137
Cs and
239,240
Pu, ha e been used o he compa isons. The ag eemen be ween bo h models
is, in gene al, a he good. Howe e , i is possible ha , due o he pa icula
beha iou s o ce ain adionuclides, ac i i y concen a ions in one o he phases
canno be calcula ed.
Acknowledgemen s
R Pe i!
aa*
nnez was suppo ed by ENRESA and he EU unde con ac FIGE-
CT2000-00085. A J Ellio was unded by he Chie Scien is ’s G oup o MAFF
unde con ac AE1021 and by he P ocu emen Execu i e o he MoD unde
con ac NPC1B/2012.
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