Biomonitoring trace metal contamination by seven sympatric alpine species in Eastern Tibetan Plateau.
Identifieur interne : 001987 ( Main/Exploration ); précédent : 001986; suivant : 001988Biomonitoring trace metal contamination by seven sympatric alpine species in Eastern Tibetan Plateau.
Auteurs : Haijian Bing [République populaire de Chine] ; Yanhong Wu [République populaire de Chine] ; Jun Zhou [République populaire de Chine] ; Hongyang Sun [République populaire de Chine]Source :
- Chemosphere [ 1879-1298 ] ; 2016.
Descripteurs français
- KwdFr :
- Arbres (composition chimique), Bryopsida (composition chimique), Couche de glace (composition chimique), Emissions des véhicules (analyse), Feuilles de plante (composition chimique), Mine (MeSH), Métaux lourds (analyse), Oligoéléments (analyse), Polluants du sol (analyse), Pollution de l'environnement (analyse), Sol (composition chimique), Surveillance de l'environnement (méthodes), Tibet (MeSH).
- MESH :
- analyse : Emissions des véhicules, Métaux lourds, Oligoéléments, Polluants du sol, Pollution de l'environnement.
- composition chimique : Arbres, Bryopsida, Couche de glace, Feuilles de plante, Sol.
- méthodes : Surveillance de l'environnement.
- Mine, Tibet.
English descriptors
- KwdEn :
- Bryopsida (chemistry), Environmental Monitoring (methods), Environmental Pollution (analysis), Ice Cover (chemistry), Metals, Heavy (analysis), Mining (MeSH), Plant Leaves (chemistry), Soil (chemistry), Soil Pollutants (analysis), Tibet (MeSH), Trace Elements (analysis), Trees (chemistry), Vehicle Emissions (analysis).
- MESH :
- chemical , analysis : Metals, Heavy, Soil Pollutants, Trace Elements, Vehicle Emissions.
- analysis : Environmental Pollution.
- chemistry : Bryopsida, Ice Cover, Plant Leaves, Soil, Trees.
- methods : Environmental Monitoring.
- Mining, Tibet.
Abstract
Biomonitoring permits determinations of trace metal contamination in remote areas like the high mountain ecosystems. In this study, six trace metals (Cd, Cr, Cu, Ni, Pb, and Zn) in seven sympatric alpine species (five tree species: Salix rehderiana, Populus purdomii, Betula albosinensis, Abies fabri, Picea brachytyla, and two dominant mosses: Pleurozium schreberi, Papillaria crocea) at the Hailuogou Glacier foreland, Eastern Tibetan Plateau, were investigated to monitor their contamination. The concentrations of trace metals and Pb isotopic ratios (206Pb/207Pb and 208Pb/206Pb) in leaves/needles, twigs, bark, roots, and mosses were determined, and the biological factors and enrichment factors were calculated. The concentrations of Cd, Cr, Pb, and Zn in mosses were significantly higher than those in tree tissues and normal plants indicating the exogenous sources. The accumulation of trace metals (except Cd and Zn) was relatively higher in the tree roots, whereas their enrichments were significant in the leaves/needles and bark. According to biological factors, enrichment factors, and factor analysis, Cd, Pb, and Zn in trees and mosses were markedly impacted by anthropogenic emissions, whereas Cr, Cu, and Ni in trees were mainly from root adsorption from soils. The Pb isotopic compositions identified the anthropogenic Pb mainly from mining and smelting, coal combustion, and vehicle exhausts. The results indicated that mosses were still priority indicator of trace metal contamination from atmospheric deposition, and the leaves and bark of S. rehderiana, P. purdomii, and B. albosinensis were the better alternatives to monitor the atmospheric contamination of trace metals in the alpine ecosystem.
DOI: 10.1016/j.chemosphere.2016.09.042
PubMed: 27668716
Affiliations:
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Electronic address: hjbing@imde.ac.cn.</nlm:affiliation><country xml:lang="fr">République populaire de Chine</country><wicri:regionArea>The Key Laboratory of Mountain Surface Processes and Ecological Regulation, Institute of Mountain Hazards and Environment, Chinese Academy of Sciences, Chengdu 610041</wicri:regionArea><wicri:noRegion>Chengdu 610041</wicri:noRegion></affiliation></author><author><name sortKey="Wu, Yanhong" sort="Wu, Yanhong" uniqKey="Wu Y" first="Yanhong" last="Wu">Yanhong Wu</name><affiliation wicri:level="1"><nlm:affiliation>The Key Laboratory of Mountain Surface Processes and Ecological Regulation, Institute of Mountain Hazards and Environment, Chinese Academy of Sciences, Chengdu 610041, China.</nlm:affiliation><country xml:lang="fr">République populaire de Chine</country><wicri:regionArea>The Key Laboratory of Mountain Surface Processes and Ecological Regulation, Institute of Mountain Hazards and Environment, Chinese Academy of Sciences, Chengdu 610041</wicri:regionArea><wicri:noRegion>Chengdu 610041</wicri:noRegion></affiliation></author><author><name sortKey="Zhou, Jun" sort="Zhou, Jun" uniqKey="Zhou J" first="Jun" last="Zhou">Jun Zhou</name><affiliation wicri:level="1"><nlm:affiliation>The Key Laboratory of Mountain Surface Processes and Ecological Regulation, Institute of Mountain Hazards and Environment, Chinese Academy of Sciences, Chengdu 610041, China.</nlm:affiliation><country xml:lang="fr">République populaire de Chine</country><wicri:regionArea>The Key Laboratory of Mountain Surface Processes and Ecological Regulation, Institute of Mountain Hazards and Environment, Chinese Academy of Sciences, Chengdu 610041</wicri:regionArea><wicri:noRegion>Chengdu 610041</wicri:noRegion></affiliation></author><author><name sortKey="Sun, Hongyang" sort="Sun, Hongyang" uniqKey="Sun H" first="Hongyang" last="Sun">Hongyang Sun</name><affiliation wicri:level="1"><nlm:affiliation>The Key Laboratory of Mountain Surface Processes and Ecological Regulation, Institute of Mountain Hazards and Environment, Chinese Academy of Sciences, Chengdu 610041, China.</nlm:affiliation><country xml:lang="fr">République populaire de Chine</country><wicri:regionArea>The Key Laboratory of Mountain Surface Processes and Ecological Regulation, Institute of Mountain Hazards and Environment, Chinese Academy of Sciences, Chengdu 610041</wicri:regionArea><wicri:noRegion>Chengdu 610041</wicri:noRegion></affiliation></author></analytic><series><title level="j">Chemosphere</title><idno type="eISSN">1879-1298</idno><imprint><date when="2016" type="published">2016</date></imprint></series></biblStruct></sourceDesc></fileDesc><profileDesc><textClass><keywords scheme="KwdEn" xml:lang="en"><term>Bryopsida (chemistry)</term><term>Environmental Monitoring (methods)</term><term>Environmental Pollution (analysis)</term><term>Ice Cover (chemistry)</term><term>Metals, Heavy (analysis)</term><term>Mining (MeSH)</term><term>Plant Leaves (chemistry)</term><term>Soil (chemistry)</term><term>Soil Pollutants (analysis)</term><term>Tibet (MeSH)</term><term>Trace Elements (analysis)</term><term>Trees (chemistry)</term><term>Vehicle Emissions (analysis)</term></keywords><keywords scheme="KwdFr" xml:lang="fr"><term>Arbres (composition chimique)</term><term>Bryopsida (composition chimique)</term><term>Couche de glace (composition chimique)</term><term>Emissions des véhicules (analyse)</term><term>Feuilles de plante (composition chimique)</term><term>Mine (MeSH)</term><term>Métaux lourds (analyse)</term><term>Oligoéléments (analyse)</term><term>Polluants du sol (analyse)</term><term>Pollution de l'environnement (analyse)</term><term>Sol (composition chimique)</term><term>Surveillance de l'environnement (méthodes)</term><term>Tibet (MeSH)</term></keywords><keywords scheme="MESH" type="chemical" qualifier="analysis" xml:lang="en"><term>Metals, Heavy</term><term>Soil Pollutants</term><term>Trace Elements</term><term>Vehicle Emissions</term></keywords><keywords scheme="MESH" qualifier="analyse" xml:lang="fr"><term>Emissions des véhicules</term><term>Métaux lourds</term><term>Oligoéléments</term><term>Polluants du sol</term><term>Pollution de l'environnement</term></keywords><keywords scheme="MESH" qualifier="analysis" xml:lang="en"><term>Environmental Pollution</term></keywords><keywords scheme="MESH" qualifier="chemistry" xml:lang="en"><term>Bryopsida</term><term>Ice Cover</term><term>Plant Leaves</term><term>Soil</term><term>Trees</term></keywords><keywords scheme="MESH" qualifier="composition chimique" xml:lang="fr"><term>Arbres</term><term>Bryopsida</term><term>Couche de glace</term><term>Feuilles de plante</term><term>Sol</term></keywords><keywords scheme="MESH" qualifier="methods" xml:lang="en"><term>Environmental Monitoring</term></keywords><keywords scheme="MESH" qualifier="méthodes" xml:lang="fr"><term>Surveillance de l'environnement</term></keywords><keywords scheme="MESH" xml:lang="en"><term>Mining</term><term>Tibet</term></keywords><keywords scheme="MESH" xml:lang="fr"><term>Mine</term><term>Tibet</term></keywords></textClass></profileDesc></teiHeader><front><div type="abstract" xml:lang="en">Biomonitoring permits determinations of trace metal contamination in remote areas like the high mountain ecosystems. In this study, six trace metals (Cd, Cr, Cu, Ni, Pb, and Zn) in seven sympatric alpine species (five tree species: Salix rehderiana, Populus purdomii, Betula albosinensis, Abies fabri, Picea brachytyla, and two dominant mosses: Pleurozium schreberi, Papillaria crocea) at the Hailuogou Glacier foreland, Eastern Tibetan Plateau, were investigated to monitor their contamination. The concentrations of trace metals and Pb isotopic ratios (<sup>206</sup>Pb/<sup>207</sup>Pb and <sup>208</sup>Pb/<sup>206</sup>Pb) in leaves/needles, twigs, bark, roots, and mosses were determined, and the biological factors and enrichment factors were calculated. The concentrations of Cd, Cr, Pb, and Zn in mosses were significantly higher than those in tree tissues and normal plants indicating the exogenous sources. The accumulation of trace metals (except Cd and Zn) was relatively higher in the tree roots, whereas their enrichments were significant in the leaves/needles and bark. According to biological factors, enrichment factors, and factor analysis, Cd, Pb, and Zn in trees and mosses were markedly impacted by anthropogenic emissions, whereas Cr, Cu, and Ni in trees were mainly from root adsorption from soils. The Pb isotopic compositions identified the anthropogenic Pb mainly from mining and smelting, coal combustion, and vehicle exhausts. The results indicated that mosses were still priority indicator of trace metal contamination from atmospheric deposition, and the leaves and bark of S. rehderiana, P. purdomii, and B. albosinensis were the better alternatives to monitor the atmospheric contamination of trace metals in the alpine ecosystem.</div></front></TEI><pubmed><MedlineCitation Status="MEDLINE" IndexingMethod="Curated" Owner="NLM"><PMID Version="1">27668716</PMID><DateCompleted><Year>2017</Year><Month>03</Month><Day>13</Day></DateCompleted><DateRevised><Year>2018</Year><Month>12</Month><Day>02</Day></DateRevised><Article PubModel="Print-Electronic"><Journal><ISSN IssnType="Electronic">1879-1298</ISSN><JournalIssue CitedMedium="Internet"><Volume>165</Volume><PubDate><Year>2016</Year><Month>Dec</Month></PubDate></JournalIssue><Title>Chemosphere</Title><ISOAbbreviation>Chemosphere</ISOAbbreviation></Journal><ArticleTitle>Biomonitoring trace metal contamination by seven sympatric alpine species in Eastern Tibetan Plateau.</ArticleTitle><Pagination><MedlinePgn>388-398</MedlinePgn></Pagination><ELocationID EIdType="pii" ValidYN="Y">S0045-6535(16)31232-2</ELocationID><ELocationID EIdType="doi" ValidYN="Y">10.1016/j.chemosphere.2016.09.042</ELocationID><Abstract><AbstractText>Biomonitoring permits determinations of trace metal contamination in remote areas like the high mountain ecosystems. In this study, six trace metals (Cd, Cr, Cu, Ni, Pb, and Zn) in seven sympatric alpine species (five tree species: Salix rehderiana, Populus purdomii, Betula albosinensis, Abies fabri, Picea brachytyla, and two dominant mosses: Pleurozium schreberi, Papillaria crocea) at the Hailuogou Glacier foreland, Eastern Tibetan Plateau, were investigated to monitor their contamination. The concentrations of trace metals and Pb isotopic ratios (<sup>206</sup>Pb/<sup>207</sup>Pb and <sup>208</sup>Pb/<sup>206</sup>Pb) in leaves/needles, twigs, bark, roots, and mosses were determined, and the biological factors and enrichment factors were calculated. The concentrations of Cd, Cr, Pb, and Zn in mosses were significantly higher than those in tree tissues and normal plants indicating the exogenous sources. The accumulation of trace metals (except Cd and Zn) was relatively higher in the tree roots, whereas their enrichments were significant in the leaves/needles and bark. According to biological factors, enrichment factors, and factor analysis, Cd, Pb, and Zn in trees and mosses were markedly impacted by anthropogenic emissions, whereas Cr, Cu, and Ni in trees were mainly from root adsorption from soils. The Pb isotopic compositions identified the anthropogenic Pb mainly from mining and smelting, coal combustion, and vehicle exhausts. The results indicated that mosses were still priority indicator of trace metal contamination from atmospheric deposition, and the leaves and bark of S. rehderiana, P. purdomii, and B. albosinensis were the better alternatives to monitor the atmospheric contamination of trace metals in the alpine ecosystem.</AbstractText><CopyrightInformation>Copyright © 2016 Elsevier Ltd. All rights reserved.</CopyrightInformation></Abstract><AuthorList CompleteYN="Y"><Author ValidYN="Y"><LastName>Bing</LastName><ForeName>Haijian</ForeName><Initials>H</Initials><AffiliationInfo><Affiliation>The Key Laboratory of Mountain Surface Processes and Ecological Regulation, Institute of Mountain Hazards and Environment, Chinese Academy of Sciences, Chengdu 610041, China. Electronic address: hjbing@imde.ac.cn.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Wu</LastName><ForeName>Yanhong</ForeName><Initials>Y</Initials><AffiliationInfo><Affiliation>The Key Laboratory of Mountain Surface Processes and Ecological Regulation, Institute of Mountain Hazards and Environment, Chinese Academy of Sciences, Chengdu 610041, China.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Zhou</LastName><ForeName>Jun</ForeName><Initials>J</Initials><AffiliationInfo><Affiliation>The Key Laboratory of Mountain Surface Processes and Ecological Regulation, Institute of Mountain Hazards and Environment, Chinese Academy of Sciences, Chengdu 610041, China.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Sun</LastName><ForeName>Hongyang</ForeName><Initials>H</Initials><AffiliationInfo><Affiliation>The Key Laboratory of Mountain Surface Processes and Ecological Regulation, Institute of Mountain Hazards and Environment, Chinese Academy of Sciences, Chengdu 610041, China.</Affiliation></AffiliationInfo></Author></AuthorList><Language>eng</Language><PublicationTypeList><PublicationType UI="D016428">Journal Article</PublicationType></PublicationTypeList><ArticleDate DateType="Electronic"><Year>2016</Year><Month>09</Month><Day>30</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="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="D014131">Trace Elements</NameOfSubstance></Chemical><Chemical><RegistryNumber>0</RegistryNumber><NameOfSubstance UI="D001335">Vehicle Emissions</NameOfSubstance></Chemical></ChemicalList><CitationSubset>IM</CitationSubset><MeshHeadingList><MeshHeading><DescriptorName UI="D019068" MajorTopicYN="N">Bryopsida</DescriptorName><QualifierName UI="Q000737" MajorTopicYN="Y">chemistry</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D004784" MajorTopicYN="N">Environmental Monitoring</DescriptorName><QualifierName UI="Q000379" MajorTopicYN="Y">methods</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D004787" MajorTopicYN="N">Environmental Pollution</DescriptorName><QualifierName UI="Q000032" MajorTopicYN="Y">analysis</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D046448" MajorTopicYN="N">Ice Cover</DescriptorName><QualifierName UI="Q000737" MajorTopicYN="N">chemistry</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D019216" MajorTopicYN="N">Metals, Heavy</DescriptorName><QualifierName UI="Q000032" MajorTopicYN="Y">analysis</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D008906" MajorTopicYN="N">Mining</DescriptorName></MeshHeading><MeshHeading><DescriptorName UI="D018515" MajorTopicYN="N">Plant Leaves</DescriptorName><QualifierName UI="Q000737" MajorTopicYN="N">chemistry</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="Q000032" MajorTopicYN="Y">analysis</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D018609" MajorTopicYN="N">Tibet</DescriptorName></MeshHeading><MeshHeading><DescriptorName UI="D014131" MajorTopicYN="N">Trace Elements</DescriptorName><QualifierName UI="Q000032" MajorTopicYN="Y">analysis</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D014197" MajorTopicYN="N">Trees</DescriptorName><QualifierName UI="Q000737" MajorTopicYN="Y">chemistry</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D001335" MajorTopicYN="N">Vehicle Emissions</DescriptorName><QualifierName UI="Q000032" MajorTopicYN="N">analysis</QualifierName></MeshHeading></MeshHeadingList><KeywordList Owner="NOTNLM"><Keyword MajorTopicYN="Y">Alpine ecosystems</Keyword><Keyword MajorTopicYN="Y">Atmospheric deposition</Keyword><Keyword MajorTopicYN="Y">Biomonitoring</Keyword><Keyword MajorTopicYN="Y">Pb isotope</Keyword><Keyword MajorTopicYN="Y">Trace metals</Keyword></KeywordList></MedlineCitation><PubmedData><History><PubMedPubDate PubStatus="received"><Year>2016</Year><Month>07</Month><Day>04</Day></PubMedPubDate><PubMedPubDate PubStatus="revised"><Year>2016</Year><Month>09</Month><Day>07</Day></PubMedPubDate><PubMedPubDate PubStatus="accepted"><Year>2016</Year><Month>09</Month><Day>12</Day></PubMedPubDate><PubMedPubDate PubStatus="pubmed"><Year>2016</Year><Month>9</Month><Day>27</Day><Hour>6</Hour><Minute>0</Minute></PubMedPubDate><PubMedPubDate PubStatus="medline"><Year>2017</Year><Month>3</Month><Day>14</Day><Hour>6</Hour><Minute>0</Minute></PubMedPubDate><PubMedPubDate PubStatus="entrez"><Year>2016</Year><Month>9</Month><Day>27</Day><Hour>6</Hour><Minute>0</Minute></PubMedPubDate></History><PublicationStatus>ppublish</PublicationStatus><ArticleIdList><ArticleId IdType="pubmed">27668716</ArticleId><ArticleId IdType="pii">S0045-6535(16)31232-2</ArticleId><ArticleId IdType="doi">10.1016/j.chemosphere.2016.09.042</ArticleId></ArticleIdList></PubmedData></pubmed><affiliations><list><country><li>République populaire de Chine</li></country></list><tree><country name="République populaire de Chine"><noRegion><name sortKey="Bing, Haijian" sort="Bing, Haijian" uniqKey="Bing H" first="Haijian" last="Bing">Haijian Bing</name></noRegion><name sortKey="Sun, Hongyang" sort="Sun, Hongyang" uniqKey="Sun H" first="Hongyang" last="Sun">Hongyang Sun</name><name sortKey="Wu, Yanhong" sort="Wu, Yanhong" uniqKey="Wu Y" first="Yanhong" last="Wu">Yanhong Wu</name><name sortKey="Zhou, Jun" sort="Zhou, Jun" uniqKey="Zhou J" first="Jun" last="Zhou">Jun Zhou</name></country></tree></affiliations></record>Pour manipuler ce document sous Unix (Dilib)
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