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Assisted phytostabilization of a multicontaminated mine technosol using biochar amendment: Early stage evaluation of biochar feedstock and particle size effects on As and Pb accumulation of two Salicaceae species (Salix viminalis and Populus euramericana).

Identifieur interne : 001044 ( Main/Exploration ); précédent : 001043; suivant : 001045

Assisted phytostabilization of a multicontaminated mine technosol using biochar amendment: Early stage evaluation of biochar feedstock and particle size effects on As and Pb accumulation of two Salicaceae species (Salix viminalis and Populus euramericana).

Auteurs : Manhattan Lebrun [Italie] ; Florie Miard [France] ; Romain Nandillon [France] ; Jean-Christophe Léger [France] ; Nour Hattab-Hambli [France] ; Gabriella S. Scippa [Italie] ; Sylvain Bourgerie [France] ; Domenico Morabito [France]

Source :

RBID : pubmed:29220748

Descripteurs français

English descriptors

Abstract

Soil contamination by metal(loid)s is one of the most important environmental problem. It leads to loss of environment biodiversity and soil functions and can have harmful effects on human health. Therefore, contaminated soils could be remediated, using phytoremediation. Indeed, plant growth will improve soil conditions while accumulating metal(loid)s and modifying their mobility. However, due to the poor fertility and high metal(loid)s levels of these soils, amendments, like biochar, has to be applied. This study was performed on a former mine technosol contaminated by As and Pb and aimed to study (i) the effect of biochar on soil physico-chemical properties and plant phytostabilization potential (ii) biochar feedstock and particle size effects. In this goal, a mesocosm experiment was set up using four different biochars, obtained from two feedstocks (lightwood and pinewood) and harboring two particle sizes (inf. 0.1 mm and 0.2-0.4 mm) and two Salicaceae species. Soil and soil pore water physico-chemical properties as well as plant growth and metal(loid)s distribution were assessed. The results showed that biochar was efficient in improving soil physico-chemical properties and reducing Pb soil pore water concentrations. This amelioration allowed plant growth and increased dry weight production of both species. Regarding metal(loid)s distribution, willow and poplar showed an As and Pb accumulation in roots and low translocation towards edible parts, i.e stems and leaves, which shows a phytostabilization potential. Finally, the 2 biochar parameters, feedstock and particle size, only affected soil and soil pore water physico-chemical properties while having no effect on plant growth.

DOI: 10.1016/j.chemosphere.2017.11.113
PubMed: 29220748


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Le document en format XML

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<term>Arsenic (metabolism)</term>
<term>Arsenic (pharmacokinetics)</term>
<term>Biodegradation, Environmental (MeSH)</term>
<term>Charcoal (chemistry)</term>
<term>Lead (metabolism)</term>
<term>Lead (pharmacokinetics)</term>
<term>Mining (MeSH)</term>
<term>Particle Size (MeSH)</term>
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<term>Populus (metabolism)</term>
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<term>Plomb (pharmacocinétique)</term>
<term>Polluants du sol (pharmacocinétique)</term>
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<div type="abstract" xml:lang="en">Soil contamination by metal(loid)s is one of the most important environmental problem. It leads to loss of environment biodiversity and soil functions and can have harmful effects on human health. Therefore, contaminated soils could be remediated, using phytoremediation. Indeed, plant growth will improve soil conditions while accumulating metal(loid)s and modifying their mobility. However, due to the poor fertility and high metal(loid)s levels of these soils, amendments, like biochar, has to be applied. This study was performed on a former mine technosol contaminated by As and Pb and aimed to study (i) the effect of biochar on soil physico-chemical properties and plant phytostabilization potential (ii) biochar feedstock and particle size effects. In this goal, a mesocosm experiment was set up using four different biochars, obtained from two feedstocks (lightwood and pinewood) and harboring two particle sizes (inf. 0.1 mm and 0.2-0.4 mm) and two Salicaceae species. Soil and soil pore water physico-chemical properties as well as plant growth and metal(loid)s distribution were assessed. The results showed that biochar was efficient in improving soil physico-chemical properties and reducing Pb soil pore water concentrations. This amelioration allowed plant growth and increased dry weight production of both species. Regarding metal(loid)s distribution, willow and poplar showed an As and Pb accumulation in roots and low translocation towards edible parts, i.e stems and leaves, which shows a phytostabilization potential. Finally, the 2 biochar parameters, feedstock and particle size, only affected soil and soil pore water physico-chemical properties while having no effect on plant growth.</div>
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<AbstractText>Soil contamination by metal(loid)s is one of the most important environmental problem. It leads to loss of environment biodiversity and soil functions and can have harmful effects on human health. Therefore, contaminated soils could be remediated, using phytoremediation. Indeed, plant growth will improve soil conditions while accumulating metal(loid)s and modifying their mobility. However, due to the poor fertility and high metal(loid)s levels of these soils, amendments, like biochar, has to be applied. This study was performed on a former mine technosol contaminated by As and Pb and aimed to study (i) the effect of biochar on soil physico-chemical properties and plant phytostabilization potential (ii) biochar feedstock and particle size effects. In this goal, a mesocosm experiment was set up using four different biochars, obtained from two feedstocks (lightwood and pinewood) and harboring two particle sizes (inf. 0.1 mm and 0.2-0.4 mm) and two Salicaceae species. Soil and soil pore water physico-chemical properties as well as plant growth and metal(loid)s distribution were assessed. The results showed that biochar was efficient in improving soil physico-chemical properties and reducing Pb soil pore water concentrations. This amelioration allowed plant growth and increased dry weight production of both species. Regarding metal(loid)s distribution, willow and poplar showed an As and Pb accumulation in roots and low translocation towards edible parts, i.e stems and leaves, which shows a phytostabilization potential. Finally, the 2 biochar parameters, feedstock and particle size, only affected soil and soil pore water physico-chemical properties while having no effect on plant growth.</AbstractText>
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<Affiliation>La Carbonerie, Crissey, France.</Affiliation>
</AffiliationInfo>
</Author>
<Author ValidYN="Y">
<LastName>Hattab-Hambli</LastName>
<ForeName>Nour</ForeName>
<Initials>N</Initials>
<AffiliationInfo>
<Affiliation>University of Orleans, INRA USC1328, LBLGC EA 1207, rue de Chartres, BP 6759, 45067, Orléans Cedex 2, France.</Affiliation>
</AffiliationInfo>
</Author>
<Author ValidYN="Y">
<LastName>Scippa</LastName>
<ForeName>Gabriella S</ForeName>
<Initials>GS</Initials>
<AffiliationInfo>
<Affiliation>Università degli Studi del Molise, Dipartimento di Bioscienze e Territorio, 86090, Pesche, Italy.</Affiliation>
</AffiliationInfo>
</Author>
<Author ValidYN="Y">
<LastName>Bourgerie</LastName>
<ForeName>Sylvain</ForeName>
<Initials>S</Initials>
<AffiliationInfo>
<Affiliation>University of Orleans, INRA USC1328, LBLGC EA 1207, rue de Chartres, BP 6759, 45067, Orléans Cedex 2, France.</Affiliation>
</AffiliationInfo>
</Author>
<Author ValidYN="Y">
<LastName>Morabito</LastName>
<ForeName>Domenico</ForeName>
<Initials>D</Initials>
<AffiliationInfo>
<Affiliation>University of Orleans, INRA USC1328, LBLGC EA 1207, rue de Chartres, BP 6759, 45067, Orléans Cedex 2, France. Electronic address: domenico.morabito@univ-orleans.fr.</Affiliation>
</AffiliationInfo>
</Author>
</AuthorList>
<Language>eng</Language>
<PublicationTypeList>
<PublicationType UI="D016428">Journal Article</PublicationType>
</PublicationTypeList>
<ArticleDate DateType="Electronic">
<Year>2017</Year>
<Month>11</Month>
<Day>28</Day>
</ArticleDate>
</Article>
<MedlineJournalInfo>
<Country>England</Country>
<MedlineTA>Chemosphere</MedlineTA>
<NlmUniqueID>0320657</NlmUniqueID>
<ISSNLinking>0045-6535</ISSNLinking>
</MedlineJournalInfo>
<ChemicalList>
<Chemical>
<RegistryNumber>0</RegistryNumber>
<NameOfSubstance UI="D012987">Soil</NameOfSubstance>
</Chemical>
<Chemical>
<RegistryNumber>0</RegistryNumber>
<NameOfSubstance UI="D012989">Soil Pollutants</NameOfSubstance>
</Chemical>
<Chemical>
<RegistryNumber>0</RegistryNumber>
<NameOfSubstance UI="C540010">biochar</NameOfSubstance>
</Chemical>
<Chemical>
<RegistryNumber>16291-96-6</RegistryNumber>
<NameOfSubstance UI="D002606">Charcoal</NameOfSubstance>
</Chemical>
<Chemical>
<RegistryNumber>2P299V784P</RegistryNumber>
<NameOfSubstance UI="D007854">Lead</NameOfSubstance>
</Chemical>
<Chemical>
<RegistryNumber>N712M78A8G</RegistryNumber>
<NameOfSubstance UI="D001151">Arsenic</NameOfSubstance>
</Chemical>
</ChemicalList>
<CitationSubset>IM</CitationSubset>
<MeshHeadingList>
<MeshHeading>
<DescriptorName UI="D001151" MajorTopicYN="N">Arsenic</DescriptorName>
<QualifierName UI="Q000378" MajorTopicYN="Y">metabolism</QualifierName>
<QualifierName UI="Q000493" MajorTopicYN="N">pharmacokinetics</QualifierName>
</MeshHeading>
<MeshHeading>
<DescriptorName UI="D001673" MajorTopicYN="N">Biodegradation, Environmental</DescriptorName>
</MeshHeading>
<MeshHeading>
<DescriptorName UI="D002606" MajorTopicYN="N">Charcoal</DescriptorName>
<QualifierName UI="Q000737" MajorTopicYN="Y">chemistry</QualifierName>
</MeshHeading>
<MeshHeading>
<DescriptorName UI="D007854" MajorTopicYN="N">Lead</DescriptorName>
<QualifierName UI="Q000378" MajorTopicYN="Y">metabolism</QualifierName>
<QualifierName UI="Q000493" MajorTopicYN="N">pharmacokinetics</QualifierName>
</MeshHeading>
<MeshHeading>
<DescriptorName UI="D008906" MajorTopicYN="N">Mining</DescriptorName>
</MeshHeading>
<MeshHeading>
<DescriptorName UI="D010316" MajorTopicYN="N">Particle Size</DescriptorName>
</MeshHeading>
<MeshHeading>
<DescriptorName UI="D032107" MajorTopicYN="N">Populus</DescriptorName>
<QualifierName UI="Q000254" MajorTopicYN="N">growth & development</QualifierName>
<QualifierName UI="Q000378" MajorTopicYN="Y">metabolism</QualifierName>
</MeshHeading>
<MeshHeading>
<DescriptorName UI="D031308" MajorTopicYN="N">Salicaceae</DescriptorName>
<QualifierName UI="Q000378" MajorTopicYN="Y">metabolism</QualifierName>
</MeshHeading>
<MeshHeading>
<DescriptorName UI="D032108" MajorTopicYN="N">Salix</DescriptorName>
<QualifierName UI="Q000378" MajorTopicYN="Y">metabolism</QualifierName>
</MeshHeading>
<MeshHeading>
<DescriptorName UI="D012987" MajorTopicYN="N">Soil</DescriptorName>
<QualifierName UI="Q000737" MajorTopicYN="N">chemistry</QualifierName>
</MeshHeading>
<MeshHeading>
<DescriptorName UI="D012989" MajorTopicYN="N">Soil Pollutants</DescriptorName>
<QualifierName UI="Q000493" MajorTopicYN="N">pharmacokinetics</QualifierName>
</MeshHeading>
</MeshHeadingList>
<KeywordList Owner="NOTNLM">
<Keyword MajorTopicYN="N">Assisted phytostabilization</Keyword>
<Keyword MajorTopicYN="N">Biochar</Keyword>
<Keyword MajorTopicYN="N">Feedstock</Keyword>
<Keyword MajorTopicYN="N">Particle size</Keyword>
<Keyword MajorTopicYN="N">Salicaceae</Keyword>
</KeywordList>
</MedlineCitation>
<PubmedData>
<History>
<PubMedPubDate PubStatus="received">
<Year>2017</Year>
<Month>08</Month>
<Day>02</Day>
</PubMedPubDate>
<PubMedPubDate PubStatus="revised">
<Year>2017</Year>
<Month>10</Month>
<Day>23</Day>
</PubMedPubDate>
<PubMedPubDate PubStatus="accepted">
<Year>2017</Year>
<Month>11</Month>
<Day>20</Day>
</PubMedPubDate>
<PubMedPubDate PubStatus="pubmed">
<Year>2017</Year>
<Month>12</Month>
<Day>9</Day>
<Hour>6</Hour>
<Minute>0</Minute>
</PubMedPubDate>
<PubMedPubDate PubStatus="medline">
<Year>2018</Year>
<Month>4</Month>
<Day>17</Day>
<Hour>6</Hour>
<Minute>0</Minute>
</PubMedPubDate>
<PubMedPubDate PubStatus="entrez">
<Year>2017</Year>
<Month>12</Month>
<Day>9</Day>
<Hour>6</Hour>
<Minute>0</Minute>
</PubMedPubDate>
</History>
<PublicationStatus>ppublish</PublicationStatus>
<ArticleIdList>
<ArticleId IdType="pubmed">29220748</ArticleId>
<ArticleId IdType="pii">S0045-6535(17)31890-8</ArticleId>
<ArticleId IdType="doi">10.1016/j.chemosphere.2017.11.113</ArticleId>
</ArticleIdList>
</PubmedData>
</pubmed>
<affiliations>
<list>
<country>
<li>France</li>
<li>Italie</li>
</country>
<region>
<li>Centre-Val de Loire</li>
<li>Région Centre</li>
</region>
<settlement>
<li>Orléans</li>
</settlement>
</list>
<tree>
<country name="Italie">
<noRegion>
<name sortKey="Lebrun, Manhattan" sort="Lebrun, Manhattan" uniqKey="Lebrun M" first="Manhattan" last="Lebrun">Manhattan Lebrun</name>
</noRegion>
<name sortKey="Scippa, Gabriella S" sort="Scippa, Gabriella S" uniqKey="Scippa G" first="Gabriella S" last="Scippa">Gabriella S. Scippa</name>
</country>
<country name="France">
<region name="Centre-Val de Loire">
<name sortKey="Miard, Florie" sort="Miard, Florie" uniqKey="Miard F" first="Florie" last="Miard">Florie Miard</name>
</region>
<name sortKey="Bourgerie, Sylvain" sort="Bourgerie, Sylvain" uniqKey="Bourgerie S" first="Sylvain" last="Bourgerie">Sylvain Bourgerie</name>
<name sortKey="Hattab Hambli, Nour" sort="Hattab Hambli, Nour" uniqKey="Hattab Hambli N" first="Nour" last="Hattab-Hambli">Nour Hattab-Hambli</name>
<name sortKey="Leger, Jean Christophe" sort="Leger, Jean Christophe" uniqKey="Leger J" first="Jean-Christophe" last="Léger">Jean-Christophe Léger</name>
<name sortKey="Morabito, Domenico" sort="Morabito, Domenico" uniqKey="Morabito D" first="Domenico" last="Morabito">Domenico Morabito</name>
<name sortKey="Nandillon, Romain" sort="Nandillon, Romain" uniqKey="Nandillon R" first="Romain" last="Nandillon">Romain Nandillon</name>
</country>
</tree>
</affiliations>
</record>

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