The Role of Nanoengineered Biochar Activated with Fe for Sulfanilamide Removal from Soils and Water
Biochar is a nanoengineered sorbent proposed to control the contamination derived from the presence of residual concentrations of sulfonamides in soil. In this work, we evaluated the sorption of sulfanilamide (SFA) in commercial biochar (BC) produced at 500 °C from oak hardwood (<i>Quercus ile...
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MDPI AG
2022-11-01
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author | Beatriz Gámiz Pilar Velarde Kurt A. Spokas Lucía Cox |
author_facet | Beatriz Gámiz Pilar Velarde Kurt A. Spokas Lucía Cox |
author_sort | Beatriz Gámiz |
collection | DOAJ |
description | Biochar is a nanoengineered sorbent proposed to control the contamination derived from the presence of residual concentrations of sulfonamides in soil. In this work, we evaluated the sorption of sulfanilamide (SFA) in commercial biochar (BC) produced at 500 °C from oak hardwood (<i>Quercus ilex</i>) and its analog activated with 2% (<i>w</i>/<i>w</i>) Fe (BC-Fe). Subsequently, the effect on dissipation and transport of SFA in untreated soil and soil treated with BC and BC-Fe was also assessed. Laboratory batch studies revealed that BC-Fe increased the sorption of SFA as compared to the pristine BC with K<sub>d</sub> of 278 and 98 L/kg, respectively. The dissipation of SFA in either untreated soil or soil treated with BC or BC-Fe was similar, displaying half-lives ranging between 4 and 6.4 days. Conversely, the concurrent determination of sorption during the incubation experiment showed that lower amounts of SFA in solution at the beginning of the experiments were bioavailable in BC-Fe-treated soil when compared to the rest of the treatments shortly after application. Leaching column studies confirmed the amendment’s capability to bind the SFA compound. Therefore, the decrease in bioavailability and movement of SFA in treated soils suggest that biochar soil application can reduce SFA soil and water contamination. According to our results, BC surface modification after Fe activation may be more appropriate for water decontamination than for soil since there were no significant differences between the two types of biochar when added to the soil. Therefore, these outcomes should be considered to optimize the SFA mitigation potential of biochar. |
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spelling | doaj.art-3986de13318b4c9b95a9b5527527b41d2023-11-24T06:03:51ZengMDPI AGMolecules1420-30492022-11-012721741810.3390/molecules27217418The Role of Nanoengineered Biochar Activated with Fe for Sulfanilamide Removal from Soils and WaterBeatriz Gámiz0Pilar Velarde1Kurt A. Spokas2Lucía Cox3Instituto de Recursos Naturales y Agrobiología de Sevilla (IRNAS), CSIC, Avenida Reina Mercedes 10, 41012 Seville, SpainInstituto de Recursos Naturales y Agrobiología de Sevilla (IRNAS), CSIC, Avenida Reina Mercedes 10, 41012 Seville, SpainU.S. Department of Agriculture, Agricultural Research Service, 439 Borlaug Hall, 1991 Upper Buford Circle, St. Paul, MN 55108, USAInstituto de Recursos Naturales y Agrobiología de Sevilla (IRNAS), CSIC, Avenida Reina Mercedes 10, 41012 Seville, SpainBiochar is a nanoengineered sorbent proposed to control the contamination derived from the presence of residual concentrations of sulfonamides in soil. In this work, we evaluated the sorption of sulfanilamide (SFA) in commercial biochar (BC) produced at 500 °C from oak hardwood (<i>Quercus ilex</i>) and its analog activated with 2% (<i>w</i>/<i>w</i>) Fe (BC-Fe). Subsequently, the effect on dissipation and transport of SFA in untreated soil and soil treated with BC and BC-Fe was also assessed. Laboratory batch studies revealed that BC-Fe increased the sorption of SFA as compared to the pristine BC with K<sub>d</sub> of 278 and 98 L/kg, respectively. The dissipation of SFA in either untreated soil or soil treated with BC or BC-Fe was similar, displaying half-lives ranging between 4 and 6.4 days. Conversely, the concurrent determination of sorption during the incubation experiment showed that lower amounts of SFA in solution at the beginning of the experiments were bioavailable in BC-Fe-treated soil when compared to the rest of the treatments shortly after application. Leaching column studies confirmed the amendment’s capability to bind the SFA compound. Therefore, the decrease in bioavailability and movement of SFA in treated soils suggest that biochar soil application can reduce SFA soil and water contamination. According to our results, BC surface modification after Fe activation may be more appropriate for water decontamination than for soil since there were no significant differences between the two types of biochar when added to the soil. Therefore, these outcomes should be considered to optimize the SFA mitigation potential of biochar.https://www.mdpi.com/1420-3049/27/21/7418activated biocharantibioticsbiodegradationbound residuesleachingnanostructured materials |
spellingShingle | Beatriz Gámiz Pilar Velarde Kurt A. Spokas Lucía Cox The Role of Nanoengineered Biochar Activated with Fe for Sulfanilamide Removal from Soils and Water Molecules activated biochar antibiotics biodegradation bound residues leaching nanostructured materials |
title | The Role of Nanoengineered Biochar Activated with Fe for Sulfanilamide Removal from Soils and Water |
title_full | The Role of Nanoengineered Biochar Activated with Fe for Sulfanilamide Removal from Soils and Water |
title_fullStr | The Role of Nanoengineered Biochar Activated with Fe for Sulfanilamide Removal from Soils and Water |
title_full_unstemmed | The Role of Nanoengineered Biochar Activated with Fe for Sulfanilamide Removal from Soils and Water |
title_short | The Role of Nanoengineered Biochar Activated with Fe for Sulfanilamide Removal from Soils and Water |
title_sort | role of nanoengineered biochar activated with fe for sulfanilamide removal from soils and water |
topic | activated biochar antibiotics biodegradation bound residues leaching nanostructured materials |
url | https://www.mdpi.com/1420-3049/27/21/7418 |
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