Popular wood and sugarcane bagasse biochars reduced uptake of chromium and lead by lettuce from mine-contaminated soil.
Identifieur interne : 000194 ( Main/Exploration ); précédent : 000193; suivant : 000195Popular wood and sugarcane bagasse biochars reduced uptake of chromium and lead by lettuce from mine-contaminated soil.
Auteurs : Amir Zeb Khan [Pakistan] ; Sardar Khan [Pakistan] ; Tehreem Ayaz [République populaire de Chine] ; Mark L. Brusseau [États-Unis] ; Muhammad Amjad Khan [Pakistan] ; Javed Nawab [Pakistan] ; Said Muhammad [Pakistan]Source :
- Environmental pollution (Barking, Essex : 1987) [ 1873-6424 ] ; 2020.
Descripteurs français
- KwdFr :
- MESH :
- analyse : Métaux lourds, Polluants du sol.
- composition chimique : Bois.
- Adulte, Cellulose, Charbon de bois, Chrome, Enfant, Humains, Laitue, Pakistan, Plomb, Saccharum, Sol, Écosystème.
- Wicri :
- geographic : Pakistan.
English descriptors
- KwdEn :
- MESH :
Abstract
As a result of metal mining activities in Pakistan, toxic heavy metals (HMs) such as chromium (Cr) and lead (Pb) often enter the soil ecosystem, accumulate in food crops and cause serious human health and environmental issues. Therefore, this study examined the efficacy of biochar for contaminated soil remediation. Poplar wood biochar (PWB) and sugarcane bagasse biochar (SCBB) were amended to mine-contaminated agricultural soil at 3% and 7% (wt/wt) application rates. Lactuca sativa (Lettuce) was cultivated in these soils in a greenhouse, and uptake of HMs (Cr and Pb) as well as biomass produced were measured. Subsequently, health risks were estimated from uptake data. When amended at 7%, both biochars significantly (P<0.01) reduced plant uptake of Cr and Pb in amended soil with significant (P<0.01) increase in biomass of lettuce as compared to the control. Risk assessment results showed that both biochars decreased the daily intake of metals (DIM) and associated health risk due to consumption of lettuce as compared to the control. The Pb human health risk index (HRI) for adults and children significantly (P<0.01) decreased with sugarcane bagasse biochar applied at 7% rate relative to other treatments (including the control). Relative to controls, the SCBB and PWB reduced Cr and Pb uptake in lettuce by 69%, 73.7%, respectively, and Pb by 57% and 47.4%, respectively. For both amendments, HRI values for Cr were within safe limits for adults and children. HRI values for Pb were not within safe limits except for the sugarcane bagasse biochar applied at 7%. Results of the study indicated that application of SCBB at 7% rate to mine impacted agricultural soil effectively increased plant biomass and reduced bioaccumulation, DIM and associated HRI of Cr and Pb as compared to other treatments and the control.
DOI: 10.1016/j.envpol.2020.114446
PubMed: 32283452
PubMed Central: PMC7654435
Affiliations:
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Le document en format XML
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Therefore, this study examined the efficacy of biochar for contaminated soil remediation. Poplar wood biochar (PWB) and sugarcane bagasse biochar (SCBB) were amended to mine-contaminated agricultural soil at 3% and 7% (wt/wt) application rates. Lactuca sativa (Lettuce) was cultivated in these soils in a greenhouse, and uptake of HMs (Cr and Pb) as well as biomass produced were measured. Subsequently, health risks were estimated from uptake data. When amended at 7%, both biochars significantly (P<0.01) reduced plant uptake of Cr and Pb in amended soil with significant (P<0.01) increase in biomass of lettuce as compared to the control. Risk assessment results showed that both biochars decreased the daily intake of metals (DIM) and associated health risk due to consumption of lettuce as compared to the control. The Pb human health risk index (HRI) for adults and children significantly (P<0.01) decreased with sugarcane bagasse biochar applied at 7% rate relative to other treatments (including the control). Relative to controls, the SCBB and PWB reduced Cr and Pb uptake in lettuce by 69%, 73.7%, respectively, and Pb by 57% and 47.4%, respectively. For both amendments, HRI values for Cr were within safe limits for adults and children. HRI values for Pb were not within safe limits except for the sugarcane bagasse biochar applied at 7%. Results of the study indicated that application of SCBB at 7% rate to mine impacted agricultural soil effectively increased plant biomass and reduced bioaccumulation, DIM and associated HRI of Cr and Pb as compared to other treatments and the control.</div></front></TEI><pubmed><MedlineCitation Status="MEDLINE" IndexingMethod="Automated" Owner="NLM"><PMID Version="1">32283452</PMID><DateCompleted><Year>2020</Year><Month>07</Month><Day>10</Day></DateCompleted><DateRevised><Year>2020</Year><Month>11</Month><Day>12</Day></DateRevised><Article PubModel="Print-Electronic"><Journal><ISSN IssnType="Electronic">1873-6424</ISSN><JournalIssue CitedMedium="Internet"><Volume>263</Volume><Issue>Pt A</Issue><PubDate><Year>2020</Year><Month>Aug</Month></PubDate></JournalIssue><Title>Environmental pollution (Barking, Essex : 1987)</Title><ISOAbbreviation>Environ Pollut</ISOAbbreviation></Journal><ArticleTitle>Popular wood and sugarcane bagasse biochars reduced uptake of chromium and lead by lettuce from mine-contaminated soil.</ArticleTitle><Pagination><MedlinePgn>114446</MedlinePgn></Pagination><ELocationID EIdType="pii" ValidYN="Y">S0269-7491(20)30403-6</ELocationID><ELocationID EIdType="doi" ValidYN="Y">10.1016/j.envpol.2020.114446</ELocationID><Abstract><AbstractText>As a result of metal mining activities in Pakistan, toxic heavy metals (HMs) such as chromium (Cr) and lead (Pb) often enter the soil ecosystem, accumulate in food crops and cause serious human health and environmental issues. Therefore, this study examined the efficacy of biochar for contaminated soil remediation. Poplar wood biochar (PWB) and sugarcane bagasse biochar (SCBB) were amended to mine-contaminated agricultural soil at 3% and 7% (wt/wt) application rates. Lactuca sativa (Lettuce) was cultivated in these soils in a greenhouse, and uptake of HMs (Cr and Pb) as well as biomass produced were measured. Subsequently, health risks were estimated from uptake data. When amended at 7%, both biochars significantly (P<0.01) reduced plant uptake of Cr and Pb in amended soil with significant (P<0.01) increase in biomass of lettuce as compared to the control. Risk assessment results showed that both biochars decreased the daily intake of metals (DIM) and associated health risk due to consumption of lettuce as compared to the control. The Pb human health risk index (HRI) for adults and children significantly (P<0.01) decreased with sugarcane bagasse biochar applied at 7% rate relative to other treatments (including the control). Relative to controls, the SCBB and PWB reduced Cr and Pb uptake in lettuce by 69%, 73.7%, respectively, and Pb by 57% and 47.4%, respectively. For both amendments, HRI values for Cr were within safe limits for adults and children. HRI values for Pb were not within safe limits except for the sugarcane bagasse biochar applied at 7%. Results of the study indicated that application of SCBB at 7% rate to mine impacted agricultural soil effectively increased plant biomass and reduced bioaccumulation, DIM and associated HRI of Cr and Pb as compared to other treatments and the control.</AbstractText><CopyrightInformation>Copyright © 2020 Elsevier Ltd. All rights reserved.</CopyrightInformation></Abstract><AuthorList CompleteYN="Y"><Author ValidYN="Y"><LastName>Khan</LastName><ForeName>Amir Zeb</ForeName><Initials>AZ</Initials><AffiliationInfo><Affiliation>Department of Environmental Sciences, University of Peshawar, 25120, Pakistan.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Khan</LastName><ForeName>Sardar</ForeName><Initials>S</Initials><AffiliationInfo><Affiliation>Department of Environmental Sciences, University of Peshawar, 25120, Pakistan. Electronic address: sardar.khan2008@yahoo.com.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Ayaz</LastName><ForeName>Tehreem</ForeName><Initials>T</Initials><AffiliationInfo><Affiliation>College of Resources and Environment, Hunan Agricultural University, Changsha, 410128, PR China.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Brusseau</LastName><ForeName>Mark L</ForeName><Initials>ML</Initials><AffiliationInfo><Affiliation>Soil, Water and Environmental Science Department, University of Arizona, Tucson, AZ85721, USA.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Khan</LastName><ForeName>Muhammad Amjad</ForeName><Initials>MA</Initials><AffiliationInfo><Affiliation>Department of Environmental Sciences, University of Peshawar, 25120, Pakistan.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Nawab</LastName><ForeName>Javed</ForeName><Initials>J</Initials><AffiliationInfo><Affiliation>Department of Environmental Sciences, Abdul Wali Khan University Mardan, Pakistan.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Muhammad</LastName><ForeName>Said</ForeName><Initials>S</Initials><AffiliationInfo><Affiliation>Environmental Geosciences, National Centre of Excellence in Geology, University of Peshawar, 25130, Pakistan.</Affiliation></AffiliationInfo></Author></AuthorList><Language>eng</Language><GrantList CompleteYN="Y"><Grant><GrantID>P42 ES004940</GrantID><Acronym>ES</Acronym><Agency>NIEHS NIH HHS</Agency><Country>United States</Country></Grant></GrantList><PublicationTypeList><PublicationType UI="D016428">Journal Article</PublicationType></PublicationTypeList><ArticleDate DateType="Electronic"><Year>2020</Year><Month>04</Month><Day>02</Day></ArticleDate></Article><MedlineJournalInfo><Country>England</Country><MedlineTA>Environ Pollut</MedlineTA><NlmUniqueID>8804476</NlmUniqueID><ISSNLinking>0269-7491</ISSNLinking></MedlineJournalInfo><ChemicalList><Chemical><RegistryNumber>0</RegistryNumber><NameOfSubstance UI="D019216">Metals, Heavy</NameOfSubstance></Chemical><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>0R0008Q3JB</RegistryNumber><NameOfSubstance UI="D002857">Chromium</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>9004-34-6</RegistryNumber><NameOfSubstance UI="D002482">Cellulose</NameOfSubstance></Chemical><Chemical><RegistryNumber>9006-97-7</RegistryNumber><NameOfSubstance UI="C027433">bagasse</NameOfSubstance></Chemical></ChemicalList><CitationSubset>IM</CitationSubset><MeshHeadingList><MeshHeading><DescriptorName UI="D000328" MajorTopicYN="N">Adult</DescriptorName></MeshHeading><MeshHeading><DescriptorName UI="D002482" MajorTopicYN="N">Cellulose</DescriptorName></MeshHeading><MeshHeading><DescriptorName UI="D002606" MajorTopicYN="N">Charcoal</DescriptorName></MeshHeading><MeshHeading><DescriptorName UI="D002648" MajorTopicYN="N">Child</DescriptorName></MeshHeading><MeshHeading><DescriptorName UI="D002857" MajorTopicYN="N">Chromium</DescriptorName></MeshHeading><MeshHeading><DescriptorName UI="D017753" MajorTopicYN="N">Ecosystem</DescriptorName></MeshHeading><MeshHeading><DescriptorName UI="D006801" MajorTopicYN="N">Humans</DescriptorName></MeshHeading><MeshHeading><DescriptorName UI="D007854" MajorTopicYN="N">Lead</DescriptorName></MeshHeading><MeshHeading><DescriptorName UI="D018545" MajorTopicYN="N">Lettuce</DescriptorName></MeshHeading><MeshHeading><DescriptorName UI="D019216" MajorTopicYN="N">Metals, Heavy</DescriptorName><QualifierName UI="Q000032" MajorTopicYN="Y">analysis</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D010154" MajorTopicYN="N" Type="Geographic">Pakistan</DescriptorName></MeshHeading><MeshHeading><DescriptorName UI="D031786" MajorTopicYN="Y">Saccharum</DescriptorName></MeshHeading><MeshHeading><DescriptorName UI="D012987" MajorTopicYN="N">Soil</DescriptorName></MeshHeading><MeshHeading><DescriptorName UI="D012989" MajorTopicYN="N">Soil Pollutants</DescriptorName><QualifierName UI="Q000032" MajorTopicYN="Y">analysis</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D014934" MajorTopicYN="N">Wood</DescriptorName><QualifierName UI="Q000737" MajorTopicYN="N">chemistry</QualifierName></MeshHeading></MeshHeadingList><KeywordList Owner="NOTNLM"><Keyword MajorTopicYN="N">Biochar</Keyword><Keyword MajorTopicYN="N">Concentration index</Keyword><Keyword MajorTopicYN="N">HMs contaminated soil</Keyword><Keyword MajorTopicYN="N">Health risk index</Keyword><Keyword MajorTopicYN="N">Lettuce</Keyword></KeywordList><CoiStatement>Declaration of competing interest The authors have no conflict of interest.</CoiStatement></MedlineCitation><PubmedData><History><PubMedPubDate PubStatus="received"><Year>2020</Year><Month>01</Month><Day>17</Day></PubMedPubDate><PubMedPubDate PubStatus="revised"><Year>2020</Year><Month>03</Month><Day>19</Day></PubMedPubDate><PubMedPubDate PubStatus="accepted"><Year>2020</Year><Month>03</Month><Day>22</Day></PubMedPubDate><PubMedPubDate PubStatus="pmc-release"><Year>2021</Year><Month>08</Month><Day>01</Day></PubMedPubDate><PubMedPubDate PubStatus="pubmed"><Year>2020</Year><Month>4</Month><Day>14</Day><Hour>6</Hour><Minute>0</Minute></PubMedPubDate><PubMedPubDate PubStatus="medline"><Year>2020</Year><Month>7</Month><Day>11</Day><Hour>6</Hour><Minute>0</Minute></PubMedPubDate><PubMedPubDate PubStatus="entrez"><Year>2020</Year><Month>4</Month><Day>14</Day><Hour>6</Hour><Minute>0</Minute></PubMedPubDate></History><PublicationStatus>ppublish</PublicationStatus><ArticleIdList><ArticleId IdType="pubmed">32283452</ArticleId><ArticleId IdType="pii">S0269-7491(20)30403-6</ArticleId><ArticleId IdType="doi">10.1016/j.envpol.2020.114446</ArticleId><ArticleId IdType="pmc">PMC7654435</ArticleId><ArticleId IdType="mid">NIHMS1640481</ArticleId></ArticleIdList><ReferenceList><Reference><Citation>Chemosphere. 2016 Feb;144:1002-11</Citation><ArticleIdList><ArticleId IdType="pubmed">26439517</ArticleId></ArticleIdList></Reference><Reference><Citation>Sci Total Environ. 2016 Jun 1;554-555:259-65</Citation><ArticleIdList><ArticleId IdType="pubmed">26950640</ArticleId></ArticleIdList></Reference><Reference><Citation>Food Chem Toxicol. 2010 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Chine</li><li>États-Unis</li></country><region><li>Arizona</li></region></list><tree><country name="Pakistan"><noRegion><name sortKey="Khan, Amir Zeb" sort="Khan, Amir Zeb" uniqKey="Khan A" first="Amir Zeb" last="Khan">Amir Zeb Khan</name></noRegion><name sortKey="Khan, Muhammad Amjad" sort="Khan, Muhammad Amjad" uniqKey="Khan M" first="Muhammad Amjad" last="Khan">Muhammad Amjad Khan</name><name sortKey="Khan, Sardar" sort="Khan, Sardar" uniqKey="Khan S" first="Sardar" last="Khan">Sardar Khan</name><name sortKey="Muhammad, Said" sort="Muhammad, Said" uniqKey="Muhammad S" first="Said" last="Muhammad">Said Muhammad</name><name sortKey="Nawab, Javed" sort="Nawab, Javed" uniqKey="Nawab J" first="Javed" last="Nawab">Javed Nawab</name></country><country name="République populaire de Chine"><noRegion><name sortKey="Ayaz, Tehreem" sort="Ayaz, Tehreem" uniqKey="Ayaz T" first="Tehreem" last="Ayaz">Tehreem Ayaz</name></noRegion></country><country name="États-Unis"><region name="Arizona"><name 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