001     48171
005     20180210123057.0
024 7 _ |2 DOI
|a 10.2136/vzj2004.0094
024 7 _ |2 WOS
|a WOS:000229799800004
037 _ _ |a PreJuSER-48171
041 _ _ |a eng
082 _ _ |a 550
084 _ _ |2 WoS
|a Environmental Sciences
084 _ _ |2 WoS
|a Soil Science
084 _ _ |2 WoS
|a Water Resources
100 1 _ |a Ritter, A.
|b 0
|0 P:(DE-HGF)0
245 _ _ |a Using TDR and inverse modeling to characterize solute transport in a layered agricultural volcanic soil
260 _ _ |a Madison, Wis.
|b SSSA
|c 2005
300 _ _ |a 300 - 309
336 7 _ |a Journal Article
|0 PUB:(DE-HGF)16
|2 PUB:(DE-HGF)
336 7 _ |a Output Types/Journal article
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336 7 _ |a Journal Article
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336 7 _ |a ARTICLE
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336 7 _ |a JOURNAL_ARTICLE
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336 7 _ |a article
|2 DRIVER
440 _ 0 |a Vadose Zone Journal
|x 1539-1663
|0 10301
|v 4
500 _ _ |a Record converted from VDB: 12.11.2012
520 _ _ |a Volcanic soils exhibit particular physical-chemical properties (i.e., strong and stable natural aggregation and high content of variable-charge minerals) that may influence solute transport. To determine if such techniques like TDR and inverse modeling are useful for analyzing solute transport in volcanic soils, we studied the governing transport processes by means of a miscible displacement experiment of Br- in a large undisturbed soil monolith. Bromide resident concentrations at several depths were monitored successfully with TDR technology, while parameters for the convective - dispersive (CDE) and mobile immobile (MIM) transport models were estimated by inverse modeling. For the relatively high soil moisture conditions, typical of high frequency-irrigation systems that we considered, Br- was found to move slowly by convection - dispersion. Simulations with the CDE and MIM transport models yielded very similar results. Although Br- is generally assumed to behave as a tracer, we found that anion in our experiment was subject to adsorption at the bottom of the monolith. This may be explained by the variable-charge nature of the minerals Fe and Al oxihydroxides) present in this volcanic soil, which exhibited anion exchange when the pH of the soil solution decreased below the zero point of charge.
536 _ _ |a Chemie und Dynamik der Geo-Biosphäre
|c U01
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|0 G:(DE-Juel1)FUEK257
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588 _ _ |a Dataset connected to Web of Science
650 _ 7 |a J
|2 WoSType
700 1 _ |a Muñoz-Carpena, R.
|b 1
|0 P:(DE-HGF)0
700 1 _ |a Regalado, C. M.
|b 2
|0 P:(DE-HGF)0
700 1 _ |a Javaux, M.
|b 3
|u FZJ
|0 P:(DE-Juel1)129477
700 1 _ |a Vanclooster, M.
|b 4
|0 P:(DE-HGF)0
773 _ _ |a 10.2136/vzj2004.0094
|g Vol. 4, p. 300 - 309
|p 300 - 309
|q 4<300 - 309
|0 PERI:(DE-600)2088189-7
|t Vadose zone journal
|v 4
|y 2005
|x 1539-1663
856 7 _ |u http://dx.doi.org/10.2136/vzj2004.0094
909 C O |o oai:juser.fz-juelich.de:48171
|p VDB
913 1 _ |k U01
|v Chemie und Dynamik der Geo-Biosphäre
|l Chemie und Dynamik der Geo-Biosphäre
|b Environment (Umwelt)
|0 G:(DE-Juel1)FUEK257
|x 0
914 1 _ |y 2005
915 _ _ |0 StatID:(DE-HGF)0010
|a JCR/ISI refereed
920 1 _ |k ICG-IV
|l Agrosphäre
|d 31.12.2006
|g ICG
|0 I:(DE-Juel1)VDB50
|x 0
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980 _ _ |a UNRESTRICTED
981 _ _ |a I:(DE-Juel1)IBG-3-20101118


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