Reactive transport modeling of the release and mobility of hexavalent chromium in a contaminated soil

Chromium-containing solid waste generated by tanning industries is an important source of hexavalent chromium (Cr(VI)) in soil and groundwater. The objective of this study is to quantify the leaching of Cr(VI) from a soil, resulting in groundwater contamination. Experiments were performed using representative soil samples obtained from the contaminated site (industrial area of the Matanza-Riachuelo basin, Argentina). A series of flow-through tests was conducted to evaluate the processes responsible for Cr(VI) release. Additionally, a column experiment allowed the study of Cr(VI) mobility along the soil profile. The experiments were performed by injecting Milli-Q water to emulate rain water under atmospheric conditions (415 ppm CO2(g) and 21% O2(g)). The variations in pH and in the concentrations of Cr(VI), Ca, S, Si and Mg with time (flow-through experiments) and with time and space (column experiment) were used to quantify the geochemical processes responsible for the mobility of Cr(VI) along the soil profile. One-dimensional (1D) numerical simulations using CrunchFlow [1] reproduced the release of Cr(VI) in the flow-through experiments and its mobility in the column experiment. Simulations indicate that dissolution of less than 3 wt% of Na2CrO4 and Cr(VI)-bearing hydrocalumite is necessary to reproduce the largest concentration of Cr(VI). Moreover, dissolution of Cr(VI)-rich ettringite, which was identified in the solid waste, contributes less Cr(VI) to the water. Furthermore, the processes of reduction and adsorption of Cr(VI) did not take place along the column.

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Bibliographic Details
Main Authors: Ceballos, Elena, Cama, Jordi, Soler, Josep M.
Format: comunicación de congreso biblioteca
Language:English
Published: European Association of Geochemistry 2023
Subjects:Reactive Transport Modeling, Ensure healthy lives and promote well-being for all at all ages, Ensure access to affordable, reliable, sustainable and modern energy for all,
Online Access:http://hdl.handle.net/10261/353091
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spelling dig-idaea-es-10261-3530912024-05-07T15:27:49Z Reactive transport modeling of the release and mobility of hexavalent chromium in a contaminated soil Ceballos, Elena Cama, Jordi Soler, Josep M. Reactive Transport Modeling Ensure healthy lives and promote well-being for all at all ages Ensure access to affordable, reliable, sustainable and modern energy for all Chromium-containing solid waste generated by tanning industries is an important source of hexavalent chromium (Cr(VI)) in soil and groundwater. The objective of this study is to quantify the leaching of Cr(VI) from a soil, resulting in groundwater contamination. Experiments were performed using representative soil samples obtained from the contaminated site (industrial area of the Matanza-Riachuelo basin, Argentina). A series of flow-through tests was conducted to evaluate the processes responsible for Cr(VI) release. Additionally, a column experiment allowed the study of Cr(VI) mobility along the soil profile. The experiments were performed by injecting Milli-Q water to emulate rain water under atmospheric conditions (415 ppm CO2(g) and 21% O2(g)). The variations in pH and in the concentrations of Cr(VI), Ca, S, Si and Mg with time (flow-through experiments) and with time and space (column experiment) were used to quantify the geochemical processes responsible for the mobility of Cr(VI) along the soil profile. One-dimensional (1D) numerical simulations using CrunchFlow [1] reproduced the release of Cr(VI) in the flow-through experiments and its mobility in the column experiment. Simulations indicate that dissolution of less than 3 wt% of Na2CrO4 and Cr(VI)-bearing hydrocalumite is necessary to reproduce the largest concentration of Cr(VI). Moreover, dissolution of Cr(VI)-rich ettringite, which was identified in the solid waste, contributes less Cr(VI) to the water. Furthermore, the processes of reduction and adsorption of Cr(VI) did not take place along the column. Peer reviewed 2024-04-08T05:52:01Z 2024-04-08T05:52:01Z 2023 comunicación de congreso http://purl.org/coar/resource_type/c_5794 Goldschmidt 2023 Abstract http://hdl.handle.net/10261/353091 10.7185/gold2023.15892 en Publisher's version https://doi.org/10.7185/gold2023.15892 Sí open European Association of Geochemistry
institution IDAEA ES
collection DSpace
country España
countrycode ES
component Bibliográfico
access En linea
databasecode dig-idaea-es
tag biblioteca
region Europa del Sur
libraryname Biblioteca del IDAEA España
language English
topic Reactive Transport Modeling
Ensure healthy lives and promote well-being for all at all ages
Ensure access to affordable, reliable, sustainable and modern energy for all
Reactive Transport Modeling
Ensure healthy lives and promote well-being for all at all ages
Ensure access to affordable, reliable, sustainable and modern energy for all
spellingShingle Reactive Transport Modeling
Ensure healthy lives and promote well-being for all at all ages
Ensure access to affordable, reliable, sustainable and modern energy for all
Reactive Transport Modeling
Ensure healthy lives and promote well-being for all at all ages
Ensure access to affordable, reliable, sustainable and modern energy for all
Ceballos, Elena
Cama, Jordi
Soler, Josep M.
Reactive transport modeling of the release and mobility of hexavalent chromium in a contaminated soil
description Chromium-containing solid waste generated by tanning industries is an important source of hexavalent chromium (Cr(VI)) in soil and groundwater. The objective of this study is to quantify the leaching of Cr(VI) from a soil, resulting in groundwater contamination. Experiments were performed using representative soil samples obtained from the contaminated site (industrial area of the Matanza-Riachuelo basin, Argentina). A series of flow-through tests was conducted to evaluate the processes responsible for Cr(VI) release. Additionally, a column experiment allowed the study of Cr(VI) mobility along the soil profile. The experiments were performed by injecting Milli-Q water to emulate rain water under atmospheric conditions (415 ppm CO2(g) and 21% O2(g)). The variations in pH and in the concentrations of Cr(VI), Ca, S, Si and Mg with time (flow-through experiments) and with time and space (column experiment) were used to quantify the geochemical processes responsible for the mobility of Cr(VI) along the soil profile. One-dimensional (1D) numerical simulations using CrunchFlow [1] reproduced the release of Cr(VI) in the flow-through experiments and its mobility in the column experiment. Simulations indicate that dissolution of less than 3 wt% of Na2CrO4 and Cr(VI)-bearing hydrocalumite is necessary to reproduce the largest concentration of Cr(VI). Moreover, dissolution of Cr(VI)-rich ettringite, which was identified in the solid waste, contributes less Cr(VI) to the water. Furthermore, the processes of reduction and adsorption of Cr(VI) did not take place along the column.
format comunicación de congreso
topic_facet Reactive Transport Modeling
Ensure healthy lives and promote well-being for all at all ages
Ensure access to affordable, reliable, sustainable and modern energy for all
author Ceballos, Elena
Cama, Jordi
Soler, Josep M.
author_facet Ceballos, Elena
Cama, Jordi
Soler, Josep M.
author_sort Ceballos, Elena
title Reactive transport modeling of the release and mobility of hexavalent chromium in a contaminated soil
title_short Reactive transport modeling of the release and mobility of hexavalent chromium in a contaminated soil
title_full Reactive transport modeling of the release and mobility of hexavalent chromium in a contaminated soil
title_fullStr Reactive transport modeling of the release and mobility of hexavalent chromium in a contaminated soil
title_full_unstemmed Reactive transport modeling of the release and mobility of hexavalent chromium in a contaminated soil
title_sort reactive transport modeling of the release and mobility of hexavalent chromium in a contaminated soil
publisher European Association of Geochemistry
publishDate 2023
url http://hdl.handle.net/10261/353091
work_keys_str_mv AT ceballoselena reactivetransportmodelingofthereleaseandmobilityofhexavalentchromiuminacontaminatedsoil
AT camajordi reactivetransportmodelingofthereleaseandmobilityofhexavalentchromiuminacontaminatedsoil
AT solerjosepm reactivetransportmodelingofthereleaseandmobilityofhexavalentchromiuminacontaminatedsoil
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