[0001] The present invention relates to a barrier against the release of radionuclides from
vitrified radioactive wastes and to the process for accomplishing it.
[0002] The liquid radioactive wastes are, presently, concentrated to dryness, incorporated
inside solid materials (glass, ceramic, cement) and then stored inside underground
cavities, wherein they are out of contact, as extensively as possible, with such agents,
as water, which tend to disperse the radionuclides. Processes are known, according
to which the radioactive wastes undergo solidification inside ceramic matrices constituted
by mixtures of Ti, Al, Zr, Ca, Ba oxides, Such crystalline materials display the advantage
of incorporating a large amount of radioactive material (up to 70%) and of being endowed
with a high corrosion strength, but suffer from the disadvantage of requiring high
costs. The most widespread processes consist in dispersing the wastes inside monolithic
shapes of glass, which are in their turn inserted inside metal containers.
[0003] Such processes are basically of three types. The first type, ICGM - "in-can glass
melting" - consists in placing both the dried radioactive wastes and the glass inside
the metal container and melting all of the material. The second type, JHGM - "joule-heated
glass melting" - involves the melting of both the wastes and the glass inside a furnace,
and the subsequent introduction of the obtained molten material inside the container.
The third type, GC -"glass-ceramic" - differs from the second one only in that the
container undergoes a high-temperature treatment, so that a partial glass crystallization
may occur.
[0004] These processes show low costs, both thanks to the wide availability of the raw material,
glass, and due to the simpleness of the processes. However the possibility exists,
in the long term, of tightness losses, by the glass, caused by the corrosive water
action - the leaching.
[0005] It was surprisingly found that the insertion of a barrier, constituted by a layer
of suitably selected oxides, between the glass and the metal container, obviates such
drawbacks. The oxides used are Al₂O₃, TiO₂, ZrO₂, either individually taken, or taken
as couples, in any percentages, or taken all together, in any percentages and in any
crystalline forms. The process for the accomplishment of such a barrier comprises
the following steps:
1) coating the inner surface of a metal container with a, preferably aqueous, suspension
of oxides selected from Al₂O₃ and/or ZrO₂ and/or TiO₂, so to form a layer having a
thickness comprised within the range of from 0.05 to 10 mm, preferably of from 0.1
mm to 3 mm.
2) concentrating to dryness, heating up to a temperature comprised within the range
of from 110 to 170°C, preferably of 150°C.
3) pouring into the metal container, processed as described under (1) and (2), the
glassy substance, as well as the radioactive wastes in either solid or molten form.
(In case the glassy substance and the wastes are poured into the container as solids,
they are molten inside the container and are then solidified according to the ICGM
and GC processes).
4) covering the upper portion by using the following procedures:
a) smear the upper glassy surface with a powder of the oxides as per point (1) and
mechanically press such a powder, so to form a compact layer having a thickness equal
to that applied onto the inner container surface.
b) place above the glassy surface a metal cover, the inner surface of which has been
previously processed as described under (1) and (2).
[0006] The process comprises moreover, as an important step besides the above mentioned
four steps, a fifth step consisting in keeping the layer of oxides (the oxide powder
applied onto the glass surface being included) and the molten glass in contact at
a temperature of from 950°C to 1350°C for a time period ranging from a few minutes
up to many hours (in particular, of 2-3 hours).
The purpose of the oxide layer is to act as a further obstacle to the contact of water
with the glass, and to bring in the nearby of, and within, the surface layers, Al³⁺,
Ti⁴⁺, Zr³⁺ ions, in as much as such ions give rise to the formation, on the same glass,
of a passivating layer, which decreases the leaching rate, up to nullifying it. From
this viewpoint, the efficaciousness of the protection is not impaired by the presence
of cracks or of a dusty consistency.
[0007] The purpose of the following Examples is to illustrate the invention; they are not
to be considered in a limitative sense.
Example 1
[0008] The inner surface of an AISI 316 stainless-steel container having a square cross
section of 2.5×2.5 cm, 1 cm high, is painted, by means of a brush, with Ceramabond
by AREMCO, an Al₂O₃ -based ceramic paint; it is then dried at 120°C. After being filled
with Pyrex type glass, it is placed inside a muffle. The container is heated to 1000°
and is kept at this temperature for half an hour. The muffle is turned off and the
sample is extracted when the temperature is of 350°C.
[0009] The Al₂O₃ layer results compact.
Example 2
[0010] The inner surface of a 3.5-cm high steel cylinder of 3.5 cm in diameter is painted,
by a brush, with an aqueous solution of alpha-Al₂O₃ (Alcoa Al6), containing 2% polyvinyl
alcohol as bonding agent. After being dried at 150°C, the cylinder is filled with
minced Pyrex and is maintained at 1050°C for 2 hrs. After turning off the muffle,
the sample is extracted when the temperature has decreased to 200°C. The coating results
unbroken.
1. Barrier against the release of radionuclides from vitrified radioactive wastes,
constituted by Al, Zr, Ti oxides, characterized in that said elements are either individually
present, or present as couples, or present all together, in any percentages and in
any crystalline forms.
2. Barrier according to claim 1, having a thickness comprised within the range of
from 0.05 mm to 10 mm, preferably of from 0.1 mm to 3 mm.
3. Process for the accomplishment of the barrier according to claims 1 and 2 consisting
in coating with a suspension of Al, Ti, Zr oxides the inner surface of a metal container,
drying at a temperature comprised within the range of from 110 to 170°C, preferably
of 150°C, pouring into the container the glass and the radioactive wastes, either
in solid or in molten form, covering the upper portion of the the mass of glass and
radioactive wastes, after melting it if it was in solid form, with the powder of the
oxides used for coating the bottom and the walls of the metal container, maintaining
the molten oxides and glass in contact for a time period of from a few minutes up
to many hours at a temperature of from 950°C to 1350°C.
4. Process according to claim 3, characterized in that the glass and the radioactive
wastes, coated with the oxides, are solidified according to the ICGM or GC processes.
5. Process according to claims 3, 4 and 5 characterized in that the upper portion
of the mass of glass and radioactive wastes is covered with the oxides applied onto
the inner face of the cover of the metal container, by the same procedure as used
to coat the inner surface of the same container.