Remediation of Pb-contaminated soil using biochar-based slow-release P fertilizer and biomonitoring employing bioindicators

Abstract Soil contamination by Pb can result from different anthropogenic sources such as lead-based paints, gasoline, pesticides, coal burning, mining, among others. This work aimed to evaluate the potential of P-loaded biochar (Biochar-based slow-release P fertilizer) to remediate a Pb-contaminate...

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Main Authors: María Paula Acosta-Luque, Julián E. López, Nancy Henao, Daniela Zapata, Juan C. Giraldo, Juan F. Saldarriaga
Format: Article
Language:English
Published: Nature Portfolio 2023-01-01
Series:Scientific Reports
Online Access:https://doi.org/10.1038/s41598-022-27043-8
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author María Paula Acosta-Luque
Julián E. López
Nancy Henao
Daniela Zapata
Juan C. Giraldo
Juan F. Saldarriaga
author_facet María Paula Acosta-Luque
Julián E. López
Nancy Henao
Daniela Zapata
Juan C. Giraldo
Juan F. Saldarriaga
author_sort María Paula Acosta-Luque
collection DOAJ
description Abstract Soil contamination by Pb can result from different anthropogenic sources such as lead-based paints, gasoline, pesticides, coal burning, mining, among others. This work aimed to evaluate the potential of P-loaded biochar (Biochar-based slow-release P fertilizer) to remediate a Pb-contaminated soil. In addition, we aim to propose a biomonitoring alternative after soil remediation. First, rice husk-derived biochar was obtained at different temperatures (450, 500, 550, and 600 °C) (raw biochars). Then, part of the resulting material was activated. Later, the raw biochars and activated biochars were immersed in a saturated KH2PO4 solution to produce P-loaded biochars. The ability of materials to immobilize Pb and increase the bioavailability of P in the soil was evaluated by an incubation test. The materials were incorporated into doses of 0.5, 1.0, and 2.0%. After 45 days, soil samples were taken to biomonitor the remediation process using two bioindicators: a phytotoxicity test and enzyme soil activity. Activated P-loaded biochar produced at 500 °C has been found to present the best conditions for soil Pb remediation. This material significantly reduced the bioavailability of Pb and increased the bioavailability of P. The phytotoxicity test and the soil enzymatic activity were significantly correlated with the decrease in bioavailable Pb but not with the increase in bioavailable P. Biomonitoring using the phytotoxicity test is a promising alternative for the evaluation of soils after remediation processes.
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spelling doaj.art-1d1f6b3ecf174a5dbcab19fde2c859fc2023-02-05T12:12:20ZengNature PortfolioScientific Reports2045-23222023-01-0113111210.1038/s41598-022-27043-8Remediation of Pb-contaminated soil using biochar-based slow-release P fertilizer and biomonitoring employing bioindicatorsMaría Paula Acosta-Luque0Julián E. López1Nancy Henao2Daniela Zapata3Juan C. Giraldo4Juan F. Saldarriaga5Department of Civil and Environmental Engineering, Universidad de los AndesFacultad de Arquitectura e Ingeniería, Institución Universitaria Colegio Mayor de AntioquiaDepartment of Civil and Environmental Engineering, Universidad de los AndesFaculty of Engineering, Universidad de MedellínFacultad de Arquitectura e Ingeniería, Institución Universitaria Colegio Mayor de AntioquiaDepartment of Civil and Environmental Engineering, Universidad de los AndesAbstract Soil contamination by Pb can result from different anthropogenic sources such as lead-based paints, gasoline, pesticides, coal burning, mining, among others. This work aimed to evaluate the potential of P-loaded biochar (Biochar-based slow-release P fertilizer) to remediate a Pb-contaminated soil. In addition, we aim to propose a biomonitoring alternative after soil remediation. First, rice husk-derived biochar was obtained at different temperatures (450, 500, 550, and 600 °C) (raw biochars). Then, part of the resulting material was activated. Later, the raw biochars and activated biochars were immersed in a saturated KH2PO4 solution to produce P-loaded biochars. The ability of materials to immobilize Pb and increase the bioavailability of P in the soil was evaluated by an incubation test. The materials were incorporated into doses of 0.5, 1.0, and 2.0%. After 45 days, soil samples were taken to biomonitor the remediation process using two bioindicators: a phytotoxicity test and enzyme soil activity. Activated P-loaded biochar produced at 500 °C has been found to present the best conditions for soil Pb remediation. This material significantly reduced the bioavailability of Pb and increased the bioavailability of P. The phytotoxicity test and the soil enzymatic activity were significantly correlated with the decrease in bioavailable Pb but not with the increase in bioavailable P. Biomonitoring using the phytotoxicity test is a promising alternative for the evaluation of soils after remediation processes.https://doi.org/10.1038/s41598-022-27043-8
spellingShingle María Paula Acosta-Luque
Julián E. López
Nancy Henao
Daniela Zapata
Juan C. Giraldo
Juan F. Saldarriaga
Remediation of Pb-contaminated soil using biochar-based slow-release P fertilizer and biomonitoring employing bioindicators
Scientific Reports
title Remediation of Pb-contaminated soil using biochar-based slow-release P fertilizer and biomonitoring employing bioindicators
title_full Remediation of Pb-contaminated soil using biochar-based slow-release P fertilizer and biomonitoring employing bioindicators
title_fullStr Remediation of Pb-contaminated soil using biochar-based slow-release P fertilizer and biomonitoring employing bioindicators
title_full_unstemmed Remediation of Pb-contaminated soil using biochar-based slow-release P fertilizer and biomonitoring employing bioindicators
title_short Remediation of Pb-contaminated soil using biochar-based slow-release P fertilizer and biomonitoring employing bioindicators
title_sort remediation of pb contaminated soil using biochar based slow release p fertilizer and biomonitoring employing bioindicators
url https://doi.org/10.1038/s41598-022-27043-8
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