Euradwaste '08 - EU Bookshop - Europa
Euradwaste '08 - EU Bookshop - Europa Euradwaste '08 - EU Bookshop - Europa
Colloid Concentration (ppm) 160 140 120 100 80 60 40 20 0 BACKppm 1.2DES 1.4DES 1.6DES 2.21 0.75 0.24 1.6 g/cm 3 Background 1.4 g/cm 3 0 100 200 300 400 500 Time (days) 1.2 g/cm 3 334 Colloid concentration (ppm) 160 140 120 100 80 60 40 20 0 Deionised water Grismel water NaCl 10 -2 M 1.2 1.4 1.6 Compaction density (g/cm 3 ) Figure 3: Left: Generation of bentonite colloids from bentonite plugs at different initial densities in deionised water. Right: Dependence on the colloid concentration with the compaction density in three different waters (deionised, Grimsel groundwater and NaCl 0.01 M. As received FEBEX clay. Ca-homoionised clay did not form colloid in appreciable concentration, but the presence of Na in the exchange complex (20 %) completely changes the generation behaviour (for example, asreceived FEBEX bentonite). Finally, the surface exposed to hydration (and the consequent existence extrusion paths) also affects colloid generation. Generated bentonite colloids are stable over month in low mineralised and alkaline pH and their stability may increase in the presence of humic acids. Neretnieks and Liu [34] suggested a ‘zero order model’ to describe the colloid generation from compacted bentonite for PA purposes. The criterion of colloid release is the critical coagulation concentration corresponding to 1 mmol/L Ca 2+ . The studies performed within FUNMIG clearly show that taking a certain Ca concentration as a colloid generation criterion does not describe the real behaviour. Calculated colloid release rates according to the ‘zero order model’ in general are by far higher than measured in experiments. The new experimental data can be used to develop an improved colloid generation model. In most of the transport studies performed in fractured cores, the breakthrough curves of colloids always presented an elution peak in a position very similar to that of conservative tracers but that their recovery critically depended on the colloid concentration and on the water flow rate (Figure 4). In the case of bentonite colloids, significant colloid filtration was observed in spite of the existence of “unfavourable” electrostatic conditions for colloid-rock attachment. In the Grimsel case, the geochemical conditions favour high colloidal stability, nonetheless, the filtration of bentonite colloid increased significantly when the hydrodynamic conditions approached the ones expected in a repository (low water flow rates) and when the roughness of the fracture surface increased [35].
Colloid Recovery (%) 100 80 60 40 20 0 Flow rate 3-6 ml/h Flow rate 6-10 ml/h Flow rate > 10 ml/h 0 20 40 60 80 100 120 140 160 180 Colloid concentration (ppm) Flow rate
- Page 300 and 301: values measured in the percolated w
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Colloid Concentration (ppm)<br />
160<br />
140<br />
120<br />
100<br />
80<br />
60<br />
40<br />
20<br />
0<br />
BACKppm<br />
1.2DES<br />
1.4DES<br />
1.6DES<br />
2.21<br />
0.75<br />
0.24<br />
1.6 g/cm 3<br />
Background<br />
1.4 g/cm 3<br />
0 100 200 300 400 500<br />
Time (days)<br />
1.2 g/cm 3<br />
334<br />
Colloid concentration (ppm)<br />
160<br />
140<br />
120<br />
100<br />
80<br />
60<br />
40<br />
20<br />
0<br />
Deionised water<br />
Grismel water<br />
NaCl 10 -2 M<br />
1.2 1.4 1.6<br />
Compaction density (g/cm 3 )<br />
Figure 3: Left: Generation of bentonite colloids from bentonite plugs at different initial densities in<br />
deionised water. Right: Dependence on the colloid concentration with the compaction density in<br />
three different waters (deionised, Grimsel groundwater and NaCl 0.01 M. As received FEBEX clay.<br />
Ca-homoionised clay did not form colloid in appreciable concentration, but the presence of Na in<br />
the exchange complex (20 %) completely changes the generation behaviour (for example, asreceived<br />
FEBEX bentonite). Finally, the surface exposed to hydration (and the consequent existence<br />
extrusion paths) also affects colloid generation. Generated bentonite colloids are stable over<br />
month in low mineralised and alkaline pH and their stability may increase in the presence of humic<br />
acids.<br />
Neretnieks and Liu [34] suggested a ‘zero order model’ to describe the colloid generation from<br />
compacted bentonite for PA purposes. The criterion of colloid release is the critical coagulation<br />
concentration corresponding to 1 mmol/L Ca 2+ . The studies performed within FUNMIG clearly<br />
show that taking a certain Ca concentration as a colloid generation criterion does not describe the<br />
real behaviour. Calculated colloid release rates according to the ‘zero order model’ in general are<br />
by far higher than measured in experiments. The new experimental data can be used to develop an<br />
improved colloid generation model.<br />
In most of the transport studies performed in fractured cores, the breakthrough curves of colloids<br />
always presented an elution peak in a position very similar to that of conservative tracers but that<br />
their recovery critically depended on the colloid concentration and on the water flow rate (Figure<br />
4).<br />
In the case of bentonite colloids, significant colloid filtration was observed in spite of the existence<br />
of “unfavourable” electrostatic conditions for colloid-rock attachment. In the Grimsel case, the geochemical<br />
conditions favour high colloidal stability, nonetheless, the filtration of bentonite colloid<br />
increased significantly when the hydrodynamic conditions approached the ones expected in a repository<br />
(low water flow rates) and when the roughness of the fracture surface increased [35].