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


     


Published online 20 April 2005
Published in J Environ Qual 34:951-962 (2005)
DOI: 10.2134/jeq2004.0295
© 2005 American Society of Agronomy, Crop Science Society of America, and Soil Science Society of America
677 S. Segoe Rd., Madison, WI 53711 USA
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 Related articles in JEQ
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 HighWire
Right arrow Citing Articles via ISI Web of Science (4)
Right arrow Citing Articles via Google Scholar
Google Scholar
Right arrow Articles by DeSutter, T. M.
Right arrow Articles by Pierzynski, G. M.
Right arrow Search for Related Content
PubMed
Right arrow PubMed Citation
Right arrow Articles by DeSutter, T. M.
Right arrow Articles by Pierzynski, G. M.
GeoRef
Right arrow GeoRef Citation
Agricola
Right arrow Articles by DeSutter, T. M.
Right arrow Articles by Pierzynski, G. M.
Related Collections
Right arrow Sorption/Exchange
Right arrow Soil Models
Right arrow Soil Chemistry
Right arrow Animal Waste
Right arrow Ground Water Quality

Evaluation of Soils for Use as Liner Materials

A Soil Chemistry Approach

Tom M. DeSuttera,b and Gary M. Pierzynskia,*

a Department of Agronomy, Throckmorton Hall, Kansas State University, Manhattan, KS 66506
b Now with the USDA-ARS National Soil Tilth Laboratory, Ames, IA 50011



View larger version (22K):

[in a new window]
 
Fig. 1. Simulation of the depth of soil (Zeq; Eq. [1]) needed to adsorb 100% of the NH4+ moving into the underlying soil of a swine-waste lagoon under various soil conditions after 1 yr. Bd, bulk density of the soil; St, whole-lagoon seepage rate; CEC, cation exchange capacity.

 


View larger version (28K):

[in a new window]
 
Fig. 2. Calcium–K+ exchange isotherms and values for the Gibb's free energy of exchange ({Delta}G) for two Great Plains soils: S1 (a) and S2 (b) alone, and with the addition of bentonite and zeolite at a concentration of 60 g kg–1. The relative percent difference (RPD) from the mean of the {Delta}G values is presented.

 


View larger version (28K):

[in a new window]
 
Fig. 3. Calcium–NH4+ exchange isotherms and values for the Gibb's free energy of exchange ({Delta}G) for two Great Plains soils: S1 (a) and S2 (b) alone, and with the addition of bentonite and zeolite at a concentration of 60 g kg–1. The relative percent difference (RPD) from the mean of the {Delta}G values is presented.

 


View larger version (26K):

[in a new window]
 
Fig. 4. Potassium–NH4+ exchange isotherms and values for the Gibb's free energy of exchange ({Delta}G) for two Great Plains soils: S1 (a) and S2 (b) alone, and with the addition of bentonite and zeolite at a concentration of 60 g kg–1. The relative percent difference (RPD) from the mean of the {Delta}G values is presented.

 


View larger version (30K):

[in a new window]
 
Fig. 5. (a) Equivalent fraction of cations on the Soil 1 (S1), Soil 1 + bentonite (S1B), and Soil 1 + zeolite (S1Z) exchanger phases predicted from the Rothmund–Kornfeld equation and Gaines–Thomas convention vs. laboratory-measured equivalent fractions on the S1, S1B, and S1Z exchangers. (b) Also with Na added to the ternary solutions at 0.013 mol L–1. Root-mean square (RMS) = [({Sigma} predicted N – measured N)2/n]0.5.

 


View larger version (30K):

[in a new window]
 
Fig. 6. (a) Equivalent fraction of cations on the Soil 2 (S2), Soil 2 + bentonite (S2B), and Soil 2 + zeolite (S2Z) exchanger phases predicted from the Rothmund–Kornfeld equation and Gaines–Thomas convention vs. laboratory-measured equivalent fractions on the S2, S2B, and S2Z exchangers. (b) Also with Na added to the ternary solutions at 0.013 mol L–1. Root-mean square (RMS) = [({Sigma} predicted N – measured N)2/n]0.5.

 





HOME HELP FEEDBACK SUBSCRIPTIONS ARCHIVE SEARCH TABLE OF CONTENTS
The SCI Journals Agronomy Journal Crop Science
Journal of Natural Resources
and Life Sciences Education
Vadose Zone Journal
Soil Science Society of America Journal Journal of Plant Registrations The Plant Genome
Copyright © 2005 by the American Society of Agronomy, Crop Science Society of America, and Soil Science Society of America.