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


     


This Article
Right arrow Abstract Freely available
Right arrow Full Text
Right arrow Full Text (PDF)
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 ISI Web of Science
Right arrow Similar articles in PubMed
Right arrow Alert me to new issues of the journal
Right arrow Download to citation manager
Citing Articles
Right arrow Citing Articles via ISI Web of Science (1)
Right arrow Citing Articles via Google Scholar
Google Scholar
Right arrow Articles by Stewart, W.M.
Right arrow Articles by Hossner, L.R.
Right arrow Search for Related Content
PubMed
Right arrow PubMed Citation
Right arrow Articles by Stewart, W.M.
Right arrow Articles by Hossner, L.R.
GeoRef
Right arrow GeoRef Citation
Agricola
Right arrow Articles by Stewart, W.M.
Right arrow Articles by Hossner, L.R.
Related Collections
Right arrow Soil Mineralogy
Right arrow Industrial Waste
Right arrow Ecological Risk Assessment
Right arrow Soil Pollution
Right arrow Soil Analysis
Right arrow Soil Methods/Instrumentation
Right arrow Soil Chemistry

Factors Affecting the Ratio of Cation Exchange Capacity to Clay Content in Lignite Overburden

W.M. Stewart and L.R. Hossner*

Department of Soil and Crop Sciences, Texas A&M University, College Station, TX 77843



View larger version (16K):

[in a new window]
 
Fig. 1. Distribution of cation exchange capacity (CEC) and percent clay values reported by a commercial laboratory for 50 overburden samples selected for general study.

 


View larger version (16K):

[in a new window]
 
Fig. 2. Comparison of percent organic C determined by a commercial laboratory (organic Cc) and percent organic C determined in the present study by difference in total C and inorganic C.

 


View larger version (19K):

[in a new window]
 
Fig. 3. Comparison of percent clay determined by a commercial laboratory (clayc) and percent clay determined after intensive dispersion.

 


View larger version (17K):

[in a new window]
 
Fig. 4. Estimated pH-dependent charge of overburden clay and the organic fraction.

 


View larger version (16K):

[in a new window]
 
Fig. 5. The relationship between the estimated cation exchange capacity (CEC) of the clay fraction after accounting for CEC due to organic C and percent clay following intensive dispersion.

 


View larger version (26K):

[in a new window]
 
Fig. 6. X-ray tracing of the fine (<0.2 µm) and coarse (0.2–2.0 µm) clay fractions from a sample dominated by smectitic clay.

 


View larger version (28K):

[in a new window]
 
Fig. 7. X-ray tracing of the fine (<0.2 µm) and coarse (0.2–2.0 µm) clay fractions from a sample dominated by kaolinitic clay.

 


View larger version (140K):

[in a new window]
 
Fig. 8. Scanning electron micrographs of shale fragments from the silt fraction of high cation exchange capacity (CEC) to percent clay samples of lignite overburden. (a) Shale fragment following overnight shaking in sodium hexametaphosphate. (b) Shale fragment following overnight shaking in sodium hexametaphosphate. (c) Shale fragment following destruction of CaCO3, organic C, Fe oxides, sonication, and shaking overnight in sodium hexametaphosphate. (d) Shale fragment following destruction of CaCO3, organic C, Fe oxides, sonication, and shaking overnight in sodium hexametaphosphate.

 





HOME HELP FEEDBACK SUBSCRIPTIONS ARCHIVE SEARCH TABLE OF CONTENTS
The SCI Journals Agronomy Journal Crop Science
Vadose Zone Journal Journal of Plant Registrations
Journal of Natural Resources
and Life Sciences Education
Soil Science Society of America Journal
Copyright © 2001 by the American Society of Agronomy, Crop Science Society of America, and Soil Science Society of America.