Using TDR and inverse modeling to characterize solute transport in a layered agricultural volcanic soil
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 vo...
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Published in | Vadose zone journal Vol. 4; no. 2; pp. 300 - 309 |
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Main Authors | , , , , |
Format | Journal Article |
Language | English |
Published |
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Soil Science Society of America
01.05.2005
Soil Science Society |
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Abstract | 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 this anion in our experiment was subject to adsorption at the bottom part 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. |
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AbstractList | 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 this anion in our experiment was subject to adsorption at the bottom part 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. 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 super(-) 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 super(-) was found to move slowly by convection- dispersion. Simulations with the CDE and MIM transport models yielded very similar results. Although Br super(-) is generally assumed to behave as a tracer, we found that this anion in our experiment was subject to adsorption at the bottom part 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. 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 this anion in our experiment was subject to adsorption at the bottom part 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. 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 this anion in our experiment was subject to adsorption at the bottom part 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. 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 this anion in our experiment was subject to adsorption at the bottom part 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. 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 this anion in our experiment was subject to adsorption at the bottom part 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. |
Author | Regalado, C.M Javaux, M Munoz-Carpena, R Vanclooster, M Ritter, A |
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Snippet | Volcanic soils exhibit particular physical-chemical properties (i.e., strong and stable natural aggregation and high content of variable-charge minerals) that... Volcanic soils exhibit particular physical‐chemical properties (i.e., strong and stable natural aggregation and high content of variable‐charge minerals) that... |
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SubjectTerms | adsorption agricultural soils agriculture aluminum aluminum oxyhydroxides Andisols anion exchange Atlantic Ocean Islands breakthrough curves bromide ion bromides bromine Canary Islands characterization chemical dispersion convection electrical methods Environmental geology field studies geochemistry geophysical methods ground water halogens inverse modeling inverse problem ion exchange iron iron oxyhydroxides layered materials layered soils mathematical models minerals miscible displacement mobility numerical models oxide, hydroxide, and oxyhydroxide minerals physicochemical properties pollution quantitative analysis reactivity simulation models soil solution soil transport processes soil water soils solute transport solutes statistical analysis TDR data Tenerife terraces time domain reflectometry tracers unsaturated zone vadose zone variable charge volcanic soils water pollution |
Title | Using TDR and inverse modeling to characterize solute transport in a layered agricultural volcanic soil |
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