SORPTION
AND DISPERSION OF STRONTIUM RADIONUCLIDE IN THE BENTONITEQUARTZ-CLAY AS
BACKFILL MATERIAL CANDIDATE ON RADIOACTIVE WASTE
The
experiment of sorption and dispersion characteristics of strontium in the
mixture of bentonite-quartz, clay quartz, bentonite-clay-quartz as candidate of
raw material for backfill material in the radioactive waste repository has been
performed. The objective of this research is to know the grain size effect of
bentonite, clay, and quartz on the weight percent ratio of bentonite to quartz,
clay to quartz, bentonite to clay to-quartz can be gives physical
characteristics of best such as bulk density (ρb), effective porosity (ε),
permeability (K), best sorption characteristic such as distribution coefficient
(Kd), and best dispersion characteristics such as dispersivity (α) and
effective dispersion coefficient (De) of strontium in the backfill material
candidate. The experiment was carried out in the column filled by the mixture
of bentonite-quartz, clay-quartz, bentonite-clay-quartz with the weight percent
ratio of bentonite to quartz, clay to quartz, bentonite to clay to quartz of 100/0,
80/20, 60/40, 40/60, 20/80, 0/100 respectively at saturated condition of water,
then flowed 0.1 N Sr(NO3)2 as buffer solution with tracer of 0.05 Ci/cm3 90Sr
as strontium radionuclide simulation was leached from immobilized radioactive
waste in the radioactive waste repository.
The concentration of 90Sr in the effluents
represented as Ct were analyzed by Ortec β counter every 30 min, then by using
profile concentration of Co and Ct, values of Kd, α and De of 90Sr in the
backfill material was determined. The experiment data showed that the best
results were -80+120 mesh grain size of bentonite, clay, quartz respectively on
the weight percent ratio of bentonite to clay to quartz of 70/10/20 with
physical characteristics of ρb = 0.658 g/cm3 , ε = 0.666 cm3 /cm3 , and K =
1.680x10-2 cm/sec, sorption characteristic of Kd = 46.108 cm3 /g, dispersion
characteristics of α = 5.443 cm, and De = 1.808x10-03 cm2 /sec can be proposed
as candidate of raw material of backfill material in the radioactive waste
repository.
EXPERIMENTAL
SECTION Materials The materials used in this experiment were bentonite has
chemical composition in the weight % as follows: H2O- (1.80%), pH at 25 °C with
10% solid (8.05%), result of dry sample at 105 °C: SiO2 (64.73%), Al2O3
(13.14%), Fe2O3 (2.92%), CaO (4.13%), MgO (1.40%), TiO2 (0.36%), K2O (1.64%),
Na2O (1.97%), H2O+ (6.03%) [7]. Whereas, quartz used in this experiment from accumulating
basin of the Sermo Kulon Progo with SiO2 content of 77.89 wt.%, and clay from
the Kasongan Bantul. Whereas as simulation of radionuclide in the radioactive
waste will be dispersed is tracer of 90Sr. The simulation of radionuclide is
90Sr tracer with concentration of 0.01 Ci/cm3 in the liquid of Sr(NO3)2 0.1 N
as buffer. Instrumentation The equipments utilized in this experiment were
sieving pans of ASTM ISO 585-R20 standard, oven Sybron, analytic balance
Sartorius, β counter Ortec, glass column, glass apparatus. Procedure
Preparation of Local Minerals (Bentonite, Quartz, Clay) Powders Gravels of
bentonite from Nanggulan Kulon Progo were dried in a oven until its constant
weight, then it was crushed to powders. The bentonite powders were poured in
the sieving pan of ASTM ISO 585-R20 standard with the sieve from upper to
bottom of 16 mesh and 30 mesh, and then were sieved. The bentonite powder grain
size of -16+30 mesh was kept on the sieving pan of 30 mesh. The same method was
used for the sieve from upper to bottom of 30 and 40 mesh, 40 and 50 mesh, 50
and 60 mesh, 60 and 70 mesh, 80 and 120 mesh respectively until the grains size
bentonite of -30+40 mesh, -40+50 mesh, -50+60 mesh, -60+70 mesh, -80+120 mesh
respectively were obtained. Preparation of quartz with SiO2 content of 77.89
wt.% from accumulating basin of Sermo Kulon Progo and clay powders from
Kasongan Bantul was carried out by the same method as that of bentonite
powders. Determination of Bulk Density of Bentonite, Quartz, and Clay Powders
by ASTM D1895B A21.A Method The bentonite powders were poured excessively into
the bowl of cylindrical glass with known volume (V) and weight (M1). The excess
of bentonite powders was scraped horizontal by using thin blade precise at
upper segment of the bowl. The bowl was filled with bentonite powders weighed
as M2. Bulk density of bentonite (ρb) is determined by equation [8]: 2 b M M V
ρ − = 1 (2) Determination of bulk density of quartz and clay powders was
carried out by the same method as that of bentonite powders.
Determination
of Effective Porosity of Bentonite, Quartz, and Clay Bed The porosity of
samples was determined by an apparatus as shown in Fig. 2. The 2 glass column
filled with the powder of single local mineral (bentonite or quartz or clay) or
the mixture of (bentonite-quartz or clay-quartz or bentonite-clay-quartz) of V1
bed volume was flowed with distilled water from burette 1 through bottom of the
2 glass column. When the distilled water stream is precisely at bed bottom of local
mineral powder at C boundary on the 2 glass column, then valve K on burette 1
was closed. Noted volume at A boundary, then distilled water was flowed to the
2 glass column filled with the local mineral powder by opening K valve. Grain Size Effect on Physical Characteristics of
Bentonite, Quartz, Clay Bed
The grain size affects the physical characteristics
of bentonite, quartz, and clay. Therefore by knowing the
grain size, the best physical properties could be
determined. Physical characteristics e.g. Bulk density
(ρb), effective porosity (ε), and permeability (k) were
showed in the Fig. 5, 6, and 7 respectively.
Fig. 5 shows that the smaller the grain sizes of
the samples, the higher its density. This case is caused
at constant volume; the smaller the grain size, the
greater total particles to fill its volume. With total of
particles increases, weight of the samples will increase
so that the greater of the bulk density such as
determined by using equation (2).
Fig. 6 shows that the smaller of grain size of
samples, the greater the porosity (ε). This case is
caused by grain size smaller in the constant bed
volume; hence total of particles will be larger. Each
particle has internal pore, and then particles to fill bed
volume to form external pore between particles.
Powders of the backfill material with smaller grain size
in the constant bed volume cause internal and external
pores greater until total of pore volumes in the bed or
usually expressed by effective porosity greater.
Effective porosity result of mineral with variation of
grain size according to experiment result expressed by
Poernomo [11-12].
Fig. 5−7 showed that bentonite, quartz and clay
with grain size of -80+120 mesh gave the bigger bulk
density, the bigger effective porosity, and the smallest
permeability. According to this result, hence bentonite,
quartz, and clay with grain size of -80+120 mesh
respectively are used as the mixture of local mineral to
determine physical characteristics in the backfill
material mixture of bentonite-quartz, clay-quartz, and
bentonite-clay-quartz. Fig. 5−7 showed that at grain
size of -80+120 mesh, bulk density of quartz > clay >
bentonite, effective porosity of quartz > clay >
bentonite, and permeability of quartz ≈ clay ≈ bentonite.
Weight Ratio Effect of Mineral Local Mixture on
Physical Characteristics
The effect of bentonite-to-quartz, clay-to-quartz,
and bentonite-to-clay-to-quartz weight ratio on physical
characteristics was showed on the Fig. 8, 9, 10
respectively.
Table 1 shows that mixture of bentonite-quartz
with the composition bentonite of 80 wt.% and quartz of
20 wt.% give best of physical characteristics (ρb, ε, K).
The mixture of clay-quartz with the composition clay of
60 wt.% and quartz of 40 wt.% gave best of physical
characteristics. The mixture of bentonite-clay-quartz
with the composition bentonite of 70 wt.%, clay of
10 wt.%, and quartz of 20 wt.% is the best of physical
characteristics.
The biggest bulk density of mineral local mixture
can increase the mechanical strength in holding canister
REFERENCE
Centre for the
Accelerator and Material Process Technology, National Nuclear Energy Agency,
Jl. Babarsari P.O. Box 6101 Ykbb Yogyakarta 55281 Received January 8, 2010;
Accepted August 30, 2010



What is the conclusion of your article, Dara?
BalasHapusRadioactive waste can be handled by means of sporption and dispersion.
HapusWhat is the purpose of this experiment?
BalasHapusThe objective of this research is to know the grain size effect of bentonite, clay, and quartz on the weight percent ratio of bentonite to quartz, clay to quartz, bentonite to clay to-quartz can be gives physical characteristics of best such as bulk density (ρb), effective porosity (ε), permeability (K), best sorption characteristic such as distribution coefficient (Kd), and best dispersion characteristics such as dispersivity (α) and effective dispersion coefficient (De) of strontium in the backfill material candidate.
HapusHow to handle the radioactive waste around us in an easy way
BalasHapusThe method of management by isolating the waste in a durable designed container placed in a temporary storage building prior to the establishment of a permanent storage location.
Hapus