Colloid Formation
and Migration (CFM)
Introduction
AIST National Instutute of Advanced Industrial Science
and Technology (Geological
Survey of Japan) ANDRA
National radioactive waste management agency, France FZk-INE
(BMWi Bundesministerium für Wirtschaft und Arbeit), Germany
JAEA
Japan Atomic Energy Agency, Japan Nagra National
Cooperative for the Disposal of Radioactive Waste
Studies of natural colloids in deep groundwaters from widely ranging
environments (eg Yucca Mountain, Wellenberg, Schwarzwald, Oklo,
Cigar Lake etc) have been ongoing for several decades. In addition,
laboratory programmes on colloid generation, stability and classical
batch experiments studying radionuclide uptake on colloids (and
the possibilities of subsequent release) have been reported and
a significant database already exists.
It is generally accepted that five requirements must be fulfilled
(the so-called colloid ladder, see below) to prove that colloid-facilitated
transport of radionuclides in a potential repository host rock may
be of significance to the long-term performance of a waste repository:
colloid ladder
As has been noted in several studies (including the recently completed
CRR, Colloid and Radionuclide
Retardation, project in the Grimsel Test Site (GTS)), the answer
to the first four questions above is probably affirmative However,
before any statements can be made about the likelihood of significant
colloid-facilitated radionuclide transport in the vicinity of a
deep geological waste repository, two points must be addressed:
first, the last question about the extent of irreversibility
of radionuclide-colloid associations must be investigated (it
could, for example, vary for different types of colloids)
second, this, and the other processes defined in the colloid
ladder, must be investigated in repository-relevant systems. Although
the in situ work carried out to date has been on a longer temporal
and spatial scale than is normally possible in laboratory experiments,
the groundwater flow velocities are 104
- 108 times greater than would be expected
in a suitable repository host rock. This is common in in situ
work ongoing around the world today and is simply a question of
practicalities (i.e. conducting in situ experiments within reasonable
timescales and budgets). Nevertheless, it could be argued that
process and mechanism understanding has now progressed to the
stage where such unrealistic experiments can provide little more
relevant information and that future work must consider significantly
longer time scales than has been the case so far and focus on,
for example, semi-stagnant groundwater systems, to better match
the conditions in and around a waste repository.