VZJ
HOME HELP FEEDBACK SUBSCRIPTIONS ARCHIVE SEARCH TABLE OF CONTENTS
 QUICK SEARCH:   [advanced]


     


This Article
Right arrow Abstract Freely available
Right arrow Full Text Free
Right arrow Full Text (PDF) Free
Right arrow Alert me when this article is cited
Right arrow Alert me if a correction is posted
Services
Right arrow Similar articles in this journal
Right arrow Similar articles in Web of Science
Right arrow Alert me to new issues of the journal
Right arrow Download to citation manager
Right arrow reprints & permissions
Citing Articles
Right arrow Citing Articles via HighWire
Right arrow Citing Articles via Google Scholar
Google Scholar
Right arrow Articles by Hu, Q.
Right arrow Articles by Wang, J. S. Y.
Right arrow Search for Related Content
PubMed
Right arrow Articles by Hu, Q.
Right arrow Articles by Wang, J. S. Y.
GeoRef
Right arrow GeoRef Citation
Agricola
Right arrow Articles by Hu, Q.
Right arrow Articles by Wang, J. S. Y.
Related Collections
Right arrow Radionuclides
Right arrow Diffusion
Right arrow Vadose Zone Processes and Chemical Transport

Characterizing Unsaturated Diffusion in Porous Tuff Gravel

Qinhong Hua,*, Timothy J. Kneafseyb, Jeffery J. Robertsa, Liviu Tomutsab and Joseph S. Y. Wangb

a 7000 East Ave., MS L-231, Lawrence Livermore National Laboratory, Livermore, CA 94550
b 1 Cyclotron Road, MS 90-1116, Lawrence Berkeley National Laboratory, Berkeley, CA 94720



View larger version (93K):

[in a new window]
 
Fig. 1. Schematic of different components of water present in an aggregate medium and their effects on diffusion. DInterior and DSurface denote interior and surface diffusion, respectively. (Modified from Conca and Wright, 1992.)

 


View larger version (24K):

[in a new window]
 
Fig. 2. Electrical conductivity measurement cell.

 


View larger version (55K):

[in a new window]
 
Fig. 3. Half-element diffusion experimental setup and schematics of microscale mapping. Face number designation is in the center of each face; Face 1 and Face 6 are the interface and far-side faces, respectively.

 


View larger version (125K):

[in a new window]
 
Fig. 4. Cross-sectional computed tomography images of two sizes of tuff gravel packed inside a column with an inner diameter of 6.22 cm: (a) 16- to 25-mm tuff gravel; (b) 6.3- to 9.5-mm tuff gravel. Spatial resolution in the viewed plane is approximately 0.2 by 0.2 mm. Voxel depth is 1 mm.

 


View larger version (129K):

[in a new window]
 
Fig. 5. One-millimeter cross-sectional computed tomography images for 6.3- to 9.5-mm tuff gravel (a) under a partially saturated condition and (b) showing water distribution (wet scan–dry scan).

 


View larger version (19K):

[in a new window]
 
Fig. 6. Diffusion coefficients versus volumetric water content for this and other work. Legend "15 mm tuff, this work (LA-ICP/MS)" includes the coefficients of surface diffusion for Br in both cubic and tetrahedral sinks (Table 2). Diffusion coefficients reported in Conca and Wright (1992) were for 86 soil and gravel samples, various bentonites, and rock core of tuff basalt and mudstone. The size of crushed tuff and silica sand was not reported (CRWMS M&O, 2000a).

 


View larger version (26K):

[in a new window]
 
Fig. 7. Tracer distributions from surface mapping using LA/ICP-MS (100-µm spot size and 10 laser pulses) for cube–cube configuration after diffusion inside nearly 100% RH chamber after 149.7 d. y axis: intensity ratio (dimensionless) denotes the signal of each tracer (solid circle: bromide; solid square: perrhenate) divided by the signal of aluminum.

 


View larger version (22K):

[in a new window]
 
Fig. 8. Tracer distributions (200-µm spot size and 20 laser pulses) on the surface of Face 3 for both source (filled symbols) and sink (open symbols) cubes inside (a) 98% RH chamber after 0.79 d and (b) 43% RH chamber after 16.3 d. x axis: 0 indicates the interface, and increasing positive number indicates increasing distance from the interface in the sink cube.

 


View larger version (19K):

[in a new window]
 
Fig. 9. Relative Br concentrations in the sink elements from 98% RH experiments. Lines are the fitted analytical diffusion solutions (Eq. [1]) with the effective diffusion coefficients shown in the legend.

 


View larger version (12K):

[in a new window]
 
Fig. 10. Adsorption isotherm of water on (a) fully hydroxylated quartz with contact angle = 0° (modified from Gee et al., 1990, Fig. 1) and (b) heat-dehydroxylated quartz with contact angle = 43° (modified from Gee et al., 1990, Fig. 2).

 





HOME HELP FEEDBACK SUBSCRIPTIONS ARCHIVE SEARCH TABLE OF CONTENTS
The SCI Journals Agronomy Journal Crop Science
Journal of Natural Resources
and Life Sciences Education
Soil Science Society of America Journal
Journal of Plant Registrations Journal of
Environmental Quality
The Plant Genome
Copyright © 2004 by the Soil Science Society of America.