C - Lublin
C - Lublin
C - Lublin
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provides the accessibility of cation exchange complex to moving soil solution and<br />
large mobile soil solution proportion than in chestnut soil. The over-compacted<br />
chestnut soil has a pore structure in which pore surfaces can rapidly become Casaturated.<br />
1.0<br />
a<br />
b<br />
C rel<br />
0.5<br />
0.0<br />
0 1 2 3<br />
V rel<br />
0 1 2 3<br />
Fig. 7. Chloride (, ), calcium (, ) and sodium (, •) breakthrough curves<br />
observed in slow-flow (hollow symbols) and fast-flow (filled symbols) experiments with<br />
two southern chernozem soil cores.<br />
In summary, the physical heterogeneity governed transport of in ions in this work.<br />
This heterogeneity may cause fast transport of adsorbing pollutants in soil profiles,<br />
groundwater pollution, and creates a challenge incorporating the physical<br />
heterogeneity in models of pollutant transport in soils and sediments.<br />
ACKNOWLEDGEMENT This work was partially supported by the Nato Science Programme,<br />
Cooperative Science & Technology Sub-Programme, Collaborative Linkage Grant # 979233.<br />
REFERENCES<br />
1.<br />
2.<br />
Barnett M.O., P.M.Jardine, S.C.Brooks, and H.M.Selim. 2000. Adsorption and transport of<br />
Uranium(VI) in subsurface media. Soil Science Society of America Journal, 64: 908-917.<br />
Danckwerts P.Y. 1953. Continuous flow systems. Distribution of residence times. Chem.<br />
Eng. Sci., 2: 47-55.<br />
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