Effect of biochar activation by different methods on toxicity of soil contaminated by industrial activity.
Identifieur interne : 000B01 ( Main/Corpus ); précédent : 000B00; suivant : 000B02Effect of biochar activation by different methods on toxicity of soil contaminated by industrial activity.
Auteurs : Michał Kołtowski ; Barbara Charmas ; Jadwiga Skubiszewska-Zi Ba ; Patryk OleszczukSource :
- Ecotoxicology and environmental safety [ 1090-2414 ] ; 2017.
English descriptors
- KwdEn :
- Aliivibrio fischeri (drug effects), Animals (MeSH), Arthropods (drug effects), Carbon Dioxide (chemistry), Charcoal (chemistry), Ecotoxicology (methods), Hot Temperature (MeSH), Lepidium sativum (drug effects), Microwaves (MeSH), Poland (MeSH), Salix (chemistry), Soil Pollutants (toxicity), Steam (MeSH).
- MESH :
- chemical , chemistry : Carbon Dioxide, Charcoal.
- chemistry : Salix.
- drug effects : Aliivibrio fischeri, Arthropods, Lepidium sativum.
- methods : Ecotoxicology.
- chemical , toxicity : Soil Pollutants.
- Animals, Hot Temperature, Microwaves, Poland, Steam.
Abstract
The objective of the study was to determine the effect of various methods of biochar activation on the ecotoxicity of soils with various properties and with various content and origin of contaminants. The biochar produced from willow (at 700°C) was activated by 1) microwaves (in a microwave reactor under an atmosphere of water vapour), 2) carbon dioxide (in the quartz fluidized bed reactor) and 3) superheated steam (in the quartz fluidized bed reactor). Three different soils were collected from industrial areas. The soils were mixed with biochar and activated biochars at the dose of 5% and ecotoxicological parameters of mixture was evaluated using two solid phase test - Phytotoxkit F (Lepidium sativum) and Collembolan test (Folsomia candida) and one liquid phase test - Microtox® (Vibrio fischeri). Biochar activation had both positive and negative impacts, depending on the activation method, kind of bioassay and kind of soil. Generally, biochar activated by microwaves increased the effectiveness of ecotoxicity reduction relative to non-activated biochars. Whereas, biochar activated with CO2 most often cause a negative effect manifested by deterioration or as a lack of improvement in relation to non-activated biochar or to non-amended soil. It was also demonstrated that the increase of biochar specific surface area caused a significant reduction of toxicity of water leachates from the studied soils. Effectiveness of the reduction of leachate toxicity was weakened in the presence of dissolved organic carbon in the soil.
DOI: 10.1016/j.ecoenv.2016.10.033
PubMed: 27842277
Links to Exploration step
pubmed:27842277Le document en format XML
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<affiliation><nlm:affiliation>Department of Environmental Chemistry, Faculty of Chemistry, Maria Curie-Skłodowska University, Pl. M. Curie-Skłodowskiej 3, 20-031 Lublin, Poland.</nlm:affiliation>
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<author><name sortKey="Charmas, Barbara" sort="Charmas, Barbara" uniqKey="Charmas B" first="Barbara" last="Charmas">Barbara Charmas</name>
<affiliation><nlm:affiliation>Department of Chromatographic Methods, Faculty of Chemistry, Maria Curie-Skłodowska University, Pl. M. Curie-Skłodowskiej 3, 20-031 Lublin, Poland.</nlm:affiliation>
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<author><name sortKey="Skubiszewska Zi Ba, Jadwiga" sort="Skubiszewska Zi Ba, Jadwiga" uniqKey="Skubiszewska Zi Ba J" first="Jadwiga" last="Skubiszewska-Zi Ba">Jadwiga Skubiszewska-Zi Ba</name>
<affiliation><nlm:affiliation>Department of Chromatographic Methods, Faculty of Chemistry, Maria Curie-Skłodowska University, Pl. M. Curie-Skłodowskiej 3, 20-031 Lublin, Poland.</nlm:affiliation>
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<author><name sortKey="Oleszczuk, Patryk" sort="Oleszczuk, Patryk" uniqKey="Oleszczuk P" first="Patryk" last="Oleszczuk">Patryk Oleszczuk</name>
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<author><name sortKey="Charmas, Barbara" sort="Charmas, Barbara" uniqKey="Charmas B" first="Barbara" last="Charmas">Barbara Charmas</name>
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<profileDesc><textClass><keywords scheme="KwdEn" xml:lang="en"><term>Aliivibrio fischeri (drug effects)</term>
<term>Animals (MeSH)</term>
<term>Arthropods (drug effects)</term>
<term>Carbon Dioxide (chemistry)</term>
<term>Charcoal (chemistry)</term>
<term>Ecotoxicology (methods)</term>
<term>Hot Temperature (MeSH)</term>
<term>Lepidium sativum (drug effects)</term>
<term>Microwaves (MeSH)</term>
<term>Poland (MeSH)</term>
<term>Salix (chemistry)</term>
<term>Soil Pollutants (toxicity)</term>
<term>Steam (MeSH)</term>
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<keywords scheme="MESH" type="chemical" qualifier="chemistry" xml:lang="en"><term>Carbon Dioxide</term>
<term>Charcoal</term>
</keywords>
<keywords scheme="MESH" qualifier="chemistry" xml:lang="en"><term>Salix</term>
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<keywords scheme="MESH" qualifier="drug effects" xml:lang="en"><term>Aliivibrio fischeri</term>
<term>Arthropods</term>
<term>Lepidium sativum</term>
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<keywords scheme="MESH" qualifier="methods" xml:lang="en"><term>Ecotoxicology</term>
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<keywords scheme="MESH" type="chemical" qualifier="toxicity" xml:lang="en"><term>Soil Pollutants</term>
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<front><div type="abstract" xml:lang="en">The objective of the study was to determine the effect of various methods of biochar activation on the ecotoxicity of soils with various properties and with various content and origin of contaminants. The biochar produced from willow (at 700°C) was activated by 1) microwaves (in a microwave reactor under an atmosphere of water vapour), 2) carbon dioxide (in the quartz fluidized bed reactor) and 3) superheated steam (in the quartz fluidized bed reactor). Three different soils were collected from industrial areas. The soils were mixed with biochar and activated biochars at the dose of 5% and ecotoxicological parameters of mixture was evaluated using two solid phase test - Phytotoxkit F (Lepidium sativum) and Collembolan test (Folsomia candida) and one liquid phase test - Microtox® (Vibrio fischeri). Biochar activation had both positive and negative impacts, depending on the activation method, kind of bioassay and kind of soil. Generally, biochar activated by microwaves increased the effectiveness of ecotoxicity reduction relative to non-activated biochars. Whereas, biochar activated with CO<sub>2</sub>
most often cause a negative effect manifested by deterioration or as a lack of improvement in relation to non-activated biochar or to non-amended soil. It was also demonstrated that the increase of biochar specific surface area caused a significant reduction of toxicity of water leachates from the studied soils. Effectiveness of the reduction of leachate toxicity was weakened in the presence of dissolved organic carbon in the soil.</div>
</front>
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<Abstract><AbstractText>The objective of the study was to determine the effect of various methods of biochar activation on the ecotoxicity of soils with various properties and with various content and origin of contaminants. The biochar produced from willow (at 700°C) was activated by 1) microwaves (in a microwave reactor under an atmosphere of water vapour), 2) carbon dioxide (in the quartz fluidized bed reactor) and 3) superheated steam (in the quartz fluidized bed reactor). Three different soils were collected from industrial areas. The soils were mixed with biochar and activated biochars at the dose of 5% and ecotoxicological parameters of mixture was evaluated using two solid phase test - Phytotoxkit F (Lepidium sativum) and Collembolan test (Folsomia candida) and one liquid phase test - Microtox® (Vibrio fischeri). Biochar activation had both positive and negative impacts, depending on the activation method, kind of bioassay and kind of soil. Generally, biochar activated by microwaves increased the effectiveness of ecotoxicity reduction relative to non-activated biochars. Whereas, biochar activated with CO<sub>2</sub>
most often cause a negative effect manifested by deterioration or as a lack of improvement in relation to non-activated biochar or to non-amended soil. It was also demonstrated that the increase of biochar specific surface area caused a significant reduction of toxicity of water leachates from the studied soils. Effectiveness of the reduction of leachate toxicity was weakened in the presence of dissolved organic carbon in the soil.</AbstractText>
<CopyrightInformation>Copyright © 2016 Elsevier Inc. All rights reserved.</CopyrightInformation>
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<AuthorList CompleteYN="Y"><Author ValidYN="Y"><LastName>Kołtowski</LastName>
<ForeName>Michał</ForeName>
<Initials>M</Initials>
<AffiliationInfo><Affiliation>Department of Environmental Chemistry, Faculty of Chemistry, Maria Curie-Skłodowska University, Pl. M. Curie-Skłodowskiej 3, 20-031 Lublin, Poland.</Affiliation>
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<Author ValidYN="Y"><LastName>Charmas</LastName>
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<AffiliationInfo><Affiliation>Department of Chromatographic Methods, Faculty of Chemistry, Maria Curie-Skłodowska University, Pl. M. Curie-Skłodowskiej 3, 20-031 Lublin, Poland.</Affiliation>
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<Author ValidYN="Y"><LastName>Skubiszewska-Zięba</LastName>
<ForeName>Jadwiga</ForeName>
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<AffiliationInfo><Affiliation>Department of Chromatographic Methods, Faculty of Chemistry, Maria Curie-Skłodowska University, Pl. M. Curie-Skłodowskiej 3, 20-031 Lublin, Poland.</Affiliation>
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<ForeName>Patryk</ForeName>
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<AffiliationInfo><Affiliation>Department of Environmental Chemistry, Faculty of Chemistry, Maria Curie-Skłodowska University, Pl. M. Curie-Skłodowskiej 3, 20-031 Lublin, Poland. Electronic address: patryk.oleszczuk@poczta.umcs.lublin.pl.</Affiliation>
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<Keyword MajorTopicYN="N">Folsomia candida</Keyword>
<Keyword MajorTopicYN="N">Lepidium sativum</Keyword>
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