Levels, accumulation patterns and retrospective trends of perfluoroalkyl acids (PFAAs) in terrestrial ecosystems over the last three decades.
Identifieur interne : 000857 ( Main/Exploration ); précédent : 000856; suivant : 000858Levels, accumulation patterns and retrospective trends of perfluoroalkyl acids (PFAAs) in terrestrial ecosystems over the last three decades.
Auteurs : Sandy Falk [Allemagne] ; Thorsten Stahl [Allemagne] ; Annette Fliedner [Allemagne] ; Heinz Rüdel [Allemagne] ; Kathrin Tarricone [Allemagne] ; Hubertus Brunn [Allemagne] ; Jan Koschorreck [Allemagne]Source :
- Environmental pollution (Barking, Essex : 1987) [ 1873-6424 ] ; 2019.
Descripteurs français
- KwdFr :
- Allemagne (MeSH), Animaux (MeSH), Cervidae (MeSH), Feuilles de plante (métabolisme), Fluorocarbones (composition chimique), Fluorocarbones (métabolisme), Foie (métabolisme), Oligochaeta (métabolisme), Polluants environnementaux (composition chimique), Polluants environnementaux (métabolisme), Surveillance de l'environnement (MeSH), Écosystème (MeSH).
- MESH :
- composition chimique : Fluorocarbones, Polluants environnementaux.
- métabolisme : Feuilles de plante, Fluorocarbones, Foie, Oligochaeta, Polluants environnementaux.
- Allemagne, Animaux, Cervidae, Surveillance de l'environnement, Écosystème.
- Wicri :
- geographic : Allemagne.
English descriptors
- KwdEn :
- Animals (MeSH), Deer (MeSH), Ecosystem (MeSH), Environmental Monitoring (MeSH), Environmental Pollutants (chemistry), Environmental Pollutants (metabolism), Fluorocarbons (chemistry), Fluorocarbons (metabolism), Germany (MeSH), Liver (metabolism), Oligochaeta (metabolism), Plant Leaves (metabolism).
- MESH :
- chemical , chemistry : Environmental Pollutants, Fluorocarbons.
- chemical , metabolism : Environmental Pollutants, Fluorocarbons.
- geographic : Germany.
- metabolism : Liver, Oligochaeta, Plant Leaves.
- Animals, Deer, Ecosystem, Environmental Monitoring.
Abstract
As a result of their ubiquitous presence in the environment perfluoroalkyl acids (PFAAs) have been demonstrated in numerous organisms worldwide, in particular in those of higher trophic levels. The fact that PFAAs have been detected in various human matrices, together with the resultant potential human health risks, knowledge of possible paths of entry and distribution in various ecosystems, is of great importance. In this context pooled samples of terrestrial ecosystems - roe deer liver (n = 141), earthworms (n = 44) as well as leaves from beech and poplar trees (n = 70) - from the year 1989-2015 were obtained from the German Environmental Specimen Bank and examined for the presence of 11 PFAAs for the first time. In addition to determining individual and total PFAA concentrations, temporal trends have been deduced in order to determine the effectiveness of regulatory measures. The highest total mean concentration of PFAAs (sum of the concentrations of the 11 analytes) were 9.9 μg/kg in the roe deer liver samples, followed by earthworm samples with a mean PFAA concentration of 3.5 μg/kg and leaves with a mean total concentration of 2.5 μg/kg. In regard to temporal trends there was a significant reduction of concentrations for perfluorooctane sulfonate, perfluorooctanoic acid, perfluorononanoic acid and perfluorodecanoic acid in roe deer liver from 2003 to 2015, an indication of the effectiveness of regulatory measures. The same is true for the perfluorooctane sulfonate concentrations in earthworms and for perfluorooctanoic acid concentrations in the leaves. In contrast, an increase in perfluorobutanoic acid concentrations was observed from 2003 to 2015 in all three matrices. In summary it must be noted that in spite of the discernible effectiveness of minimization strategies, PFAAs are still detectable in terrestrial matrices and concentrations of other PFAAs as perfluorobutanoic acid appear to be increasing.
DOI: 10.1016/j.envpol.2018.12.095
PubMed: 31159142
Affiliations:
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Biogeography/ Envrionmental Specimen Bank, Universitätsring 15, 54296, Trier, Germany.</nlm:affiliation><country xml:lang="fr">Allemagne</country><wicri:regionArea>Trier University, FB VI - Biogeography/ Envrionmental Specimen Bank, Universitätsring 15, 54296, Trier</wicri:regionArea><wicri:noRegion>54296, Trier</wicri:noRegion><wicri:noRegion>54296, Trier</wicri:noRegion><wicri:noRegion>Trier</wicri:noRegion></affiliation></author><author><name sortKey="Brunn, Hubertus" sort="Brunn, Hubertus" uniqKey="Brunn H" first="Hubertus" last="Brunn">Hubertus Brunn</name><affiliation wicri:level="1"><nlm:affiliation>Hessian State Laboratory, Schuberstr. 60, 35392, Gießen, Germany.</nlm:affiliation><country xml:lang="fr">Allemagne</country><wicri:regionArea>Hessian State Laboratory, Schuberstr. 60, 35392, Gießen</wicri:regionArea><wicri:noRegion>35392, Gießen</wicri:noRegion><wicri:noRegion>35392, Gießen</wicri:noRegion><wicri:noRegion>Gießen</wicri:noRegion></affiliation></author><author><name sortKey="Koschorreck, Jan" sort="Koschorreck, Jan" uniqKey="Koschorreck J" first="Jan" last="Koschorreck">Jan Koschorreck</name><affiliation wicri:level="3"><nlm:affiliation>German Environment Agency, Bismarckplatz 1, D-14193, Berlin, Germany.</nlm:affiliation><country xml:lang="fr">Allemagne</country><wicri:regionArea>German Environment Agency, Bismarckplatz 1, D-14193, Berlin</wicri:regionArea><placeName><region type="land" nuts="3">Berlin</region><settlement type="city">Berlin</settlement></placeName></affiliation></author></analytic><series><title level="j">Environmental pollution (Barking, Essex : 1987)</title><idno type="eISSN">1873-6424</idno><imprint><date when="2019" type="published">2019</date></imprint></series></biblStruct></sourceDesc></fileDesc><profileDesc><textClass><keywords scheme="KwdEn" xml:lang="en"><term>Animals (MeSH)</term><term>Deer (MeSH)</term><term>Ecosystem (MeSH)</term><term>Environmental Monitoring (MeSH)</term><term>Environmental Pollutants (chemistry)</term><term>Environmental Pollutants (metabolism)</term><term>Fluorocarbons (chemistry)</term><term>Fluorocarbons (metabolism)</term><term>Germany (MeSH)</term><term>Liver (metabolism)</term><term>Oligochaeta (metabolism)</term><term>Plant Leaves (metabolism)</term></keywords><keywords scheme="KwdFr" xml:lang="fr"><term>Allemagne (MeSH)</term><term>Animaux (MeSH)</term><term>Cervidae (MeSH)</term><term>Feuilles de plante (métabolisme)</term><term>Fluorocarbones (composition chimique)</term><term>Fluorocarbones (métabolisme)</term><term>Foie (métabolisme)</term><term>Oligochaeta (métabolisme)</term><term>Polluants environnementaux (composition chimique)</term><term>Polluants environnementaux (métabolisme)</term><term>Surveillance de l'environnement (MeSH)</term><term>Écosystème (MeSH)</term></keywords><keywords scheme="MESH" type="chemical" qualifier="chemistry" xml:lang="en"><term>Environmental Pollutants</term><term>Fluorocarbons</term></keywords><keywords scheme="MESH" type="chemical" qualifier="metabolism" xml:lang="en"><term>Environmental Pollutants</term><term>Fluorocarbons</term></keywords><keywords scheme="MESH" type="geographic" xml:lang="en"><term>Germany</term></keywords><keywords scheme="MESH" qualifier="composition chimique" xml:lang="fr"><term>Fluorocarbones</term><term>Polluants environnementaux</term></keywords><keywords scheme="MESH" qualifier="metabolism" xml:lang="en"><term>Liver</term><term>Oligochaeta</term><term>Plant Leaves</term></keywords><keywords scheme="MESH" qualifier="métabolisme" xml:lang="fr"><term>Feuilles de plante</term><term>Fluorocarbones</term><term>Foie</term><term>Oligochaeta</term><term>Polluants environnementaux</term></keywords><keywords scheme="MESH" xml:lang="en"><term>Animals</term><term>Deer</term><term>Ecosystem</term><term>Environmental Monitoring</term></keywords><keywords scheme="MESH" xml:lang="fr"><term>Allemagne</term><term>Animaux</term><term>Cervidae</term><term>Surveillance de l'environnement</term><term>Écosystème</term></keywords><keywords scheme="Wicri" type="geographic" xml:lang="fr"><term>Allemagne</term></keywords></textClass></profileDesc></teiHeader><front><div type="abstract" xml:lang="en">As a result of their ubiquitous presence in the environment perfluoroalkyl acids (PFAAs) have been demonstrated in numerous organisms worldwide, in particular in those of higher trophic levels. The fact that PFAAs have been detected in various human matrices, together with the resultant potential human health risks, knowledge of possible paths of entry and distribution in various ecosystems, is of great importance. In this context pooled samples of terrestrial ecosystems - roe deer liver (n = 141), earthworms (n = 44) as well as leaves from beech and poplar trees (n = 70) - from the year 1989-2015 were obtained from the German Environmental Specimen Bank and examined for the presence of 11 PFAAs for the first time. In addition to determining individual and total PFAA concentrations, temporal trends have been deduced in order to determine the effectiveness of regulatory measures. The highest total mean concentration of PFAAs (sum of the concentrations of the 11 analytes) were 9.9 μg/kg in the roe deer liver samples, followed by earthworm samples with a mean PFAA concentration of 3.5 μg/kg and leaves with a mean total concentration of 2.5 μg/kg. In regard to temporal trends there was a significant reduction of concentrations for perfluorooctane sulfonate, perfluorooctanoic acid, perfluorononanoic acid and perfluorodecanoic acid in roe deer liver from 2003 to 2015, an indication of the effectiveness of regulatory measures. The same is true for the perfluorooctane sulfonate concentrations in earthworms and for perfluorooctanoic acid concentrations in the leaves. In contrast, an increase in perfluorobutanoic acid concentrations was observed from 2003 to 2015 in all three matrices. In summary it must be noted that in spite of the discernible effectiveness of minimization strategies, PFAAs are still detectable in terrestrial matrices and concentrations of other PFAAs as perfluorobutanoic acid appear to be increasing.</div></front></TEI><pubmed><MedlineCitation Status="MEDLINE" IndexingMethod="Curated" Owner="NLM"><PMID Version="1">31159142</PMID><DateCompleted><Year>2019</Year><Month>08</Month><Day>06</Day></DateCompleted><DateRevised><Year>2019</Year><Month>08</Month><Day>06</Day></DateRevised><Article PubModel="Print-Electronic"><Journal><ISSN IssnType="Electronic">1873-6424</ISSN><JournalIssue CitedMedium="Internet"><Volume>246</Volume><PubDate><Year>2019</Year><Month>Mar</Month></PubDate></JournalIssue><Title>Environmental pollution (Barking, Essex : 1987)</Title><ISOAbbreviation>Environ Pollut</ISOAbbreviation></Journal><ArticleTitle>Levels, accumulation patterns and retrospective trends of perfluoroalkyl acids (PFAAs) in terrestrial ecosystems over the last three decades.</ArticleTitle><Pagination><MedlinePgn>921-931</MedlinePgn></Pagination><ELocationID EIdType="pii" ValidYN="Y">S0269-7491(18)34006-5</ELocationID><ELocationID EIdType="doi" ValidYN="Y">10.1016/j.envpol.2018.12.095</ELocationID><Abstract><AbstractText>As a result of their ubiquitous presence in the environment perfluoroalkyl acids (PFAAs) have been demonstrated in numerous organisms worldwide, in particular in those of higher trophic levels. The fact that PFAAs have been detected in various human matrices, together with the resultant potential human health risks, knowledge of possible paths of entry and distribution in various ecosystems, is of great importance. In this context pooled samples of terrestrial ecosystems - roe deer liver (n = 141), earthworms (n = 44) as well as leaves from beech and poplar trees (n = 70) - from the year 1989-2015 were obtained from the German Environmental Specimen Bank and examined for the presence of 11 PFAAs for the first time. In addition to determining individual and total PFAA concentrations, temporal trends have been deduced in order to determine the effectiveness of regulatory measures. The highest total mean concentration of PFAAs (sum of the concentrations of the 11 analytes) were 9.9 μg/kg in the roe deer liver samples, followed by earthworm samples with a mean PFAA concentration of 3.5 μg/kg and leaves with a mean total concentration of 2.5 μg/kg. In regard to temporal trends there was a significant reduction of concentrations for perfluorooctane sulfonate, perfluorooctanoic acid, perfluorononanoic acid and perfluorodecanoic acid in roe deer liver from 2003 to 2015, an indication of the effectiveness of regulatory measures. The same is true for the perfluorooctane sulfonate concentrations in earthworms and for perfluorooctanoic acid concentrations in the leaves. In contrast, an increase in perfluorobutanoic acid concentrations was observed from 2003 to 2015 in all three matrices. In summary it must be noted that in spite of the discernible effectiveness of minimization strategies, PFAAs are still detectable in terrestrial matrices and concentrations of other PFAAs as perfluorobutanoic acid appear to be increasing.</AbstractText><CopyrightInformation>Copyright © 2019 Elsevier Ltd. All rights reserved.</CopyrightInformation></Abstract><AuthorList CompleteYN="Y"><Author ValidYN="Y"><LastName>Falk</LastName><ForeName>Sandy</ForeName><Initials>S</Initials><AffiliationInfo><Affiliation>Hessian State Laboratory, Glarusstr. 6, D-65203, Wiesbaden, Germany. Electronic address: sandy.falk@lhl.hessen.de.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Stahl</LastName><ForeName>Thorsten</ForeName><Initials>T</Initials><AffiliationInfo><Affiliation>Hessian State Laboratory, Am Versuchsfeld 11-13, D-34128, Kassel, Germany.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Fliedner</LastName><ForeName>Annette</ForeName><Initials>A</Initials><AffiliationInfo><Affiliation>Fraunhofer Institute for Molecular Biology and Applied Ecology IME, Auf dem Aberg 1, 57392, Schmallenberg, Germany.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Rüdel</LastName><ForeName>Heinz</ForeName><Initials>H</Initials><AffiliationInfo><Affiliation>Fraunhofer Institute for Molecular Biology and Applied Ecology IME, Auf dem Aberg 1, 57392, Schmallenberg, Germany.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Tarricone</LastName><ForeName>Kathrin</ForeName><Initials>K</Initials><AffiliationInfo><Affiliation>Trier University, FB VI - Biogeography/ Envrionmental Specimen Bank, Universitätsring 15, 54296, Trier, Germany.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Brunn</LastName><ForeName>Hubertus</ForeName><Initials>H</Initials><AffiliationInfo><Affiliation>Hessian State Laboratory, Schuberstr. 60, 35392, Gießen, Germany.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Koschorreck</LastName><ForeName>Jan</ForeName><Initials>J</Initials><AffiliationInfo><Affiliation>German Environment Agency, Bismarckplatz 1, D-14193, Berlin, Germany.</Affiliation></AffiliationInfo></Author></AuthorList><Language>eng</Language><PublicationTypeList><PublicationType UI="D016428">Journal Article</PublicationType></PublicationTypeList><ArticleDate DateType="Electronic"><Year>2019</Year><Month>01</Month><Day>03</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="D004785">Environmental Pollutants</NameOfSubstance></Chemical><Chemical><RegistryNumber>0</RegistryNumber><NameOfSubstance UI="D005466">Fluorocarbons</NameOfSubstance></Chemical></ChemicalList><MeshHeadingList><MeshHeading><DescriptorName UI="D000818" MajorTopicYN="N">Animals</DescriptorName></MeshHeading><MeshHeading><DescriptorName UI="D003670" MajorTopicYN="N">Deer</DescriptorName></MeshHeading><MeshHeading><DescriptorName UI="D017753" MajorTopicYN="Y">Ecosystem</DescriptorName></MeshHeading><MeshHeading><DescriptorName UI="D004784" MajorTopicYN="Y">Environmental Monitoring</DescriptorName></MeshHeading><MeshHeading><DescriptorName UI="D004785" MajorTopicYN="N">Environmental Pollutants</DescriptorName><QualifierName UI="Q000737" MajorTopicYN="N">chemistry</QualifierName><QualifierName UI="Q000378" MajorTopicYN="Y">metabolism</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D005466" MajorTopicYN="N">Fluorocarbons</DescriptorName><QualifierName UI="Q000737" MajorTopicYN="N">chemistry</QualifierName><QualifierName UI="Q000378" MajorTopicYN="Y">metabolism</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D005858" MajorTopicYN="N" Type="Geographic">Germany</DescriptorName></MeshHeading><MeshHeading><DescriptorName UI="D008099" MajorTopicYN="N">Liver</DescriptorName><QualifierName UI="Q000378" MajorTopicYN="N">metabolism</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D009835" MajorTopicYN="N">Oligochaeta</DescriptorName><QualifierName UI="Q000378" MajorTopicYN="N">metabolism</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D018515" MajorTopicYN="N">Plant Leaves</DescriptorName><QualifierName UI="Q000378" MajorTopicYN="N">metabolism</QualifierName></MeshHeading></MeshHeadingList><KeywordList Owner="NOTNLM"><Keyword MajorTopicYN="N">Earthworm</Keyword><Keyword MajorTopicYN="N">Leaves</Keyword><Keyword MajorTopicYN="N">Roe deer liver</Keyword><Keyword MajorTopicYN="N">Temporal trends for PFAAs</Keyword><Keyword MajorTopicYN="N">Terrestrial ecosystem</Keyword></KeywordList></MedlineCitation><PubmedData><History><PubMedPubDate PubStatus="received"><Year>2018</Year><Month>09</Month><Day>19</Day></PubMedPubDate><PubMedPubDate PubStatus="revised"><Year>2018</Year><Month>12</Month><Day>21</Day></PubMedPubDate><PubMedPubDate PubStatus="accepted"><Year>2018</Year><Month>12</Month><Day>31</Day></PubMedPubDate><PubMedPubDate PubStatus="entrez"><Year>2019</Year><Month>6</Month><Day>5</Day><Hour>6</Hour><Minute>0</Minute></PubMedPubDate><PubMedPubDate PubStatus="pubmed"><Year>2019</Year><Month>6</Month><Day>5</Day><Hour>6</Hour><Minute>0</Minute></PubMedPubDate><PubMedPubDate PubStatus="medline"><Year>2019</Year><Month>8</Month><Day>7</Day><Hour>6</Hour><Minute>0</Minute></PubMedPubDate></History><PublicationStatus>ppublish</PublicationStatus><ArticleIdList><ArticleId IdType="pubmed">31159142</ArticleId><ArticleId IdType="pii">S0269-7491(18)34006-5</ArticleId><ArticleId IdType="doi">10.1016/j.envpol.2018.12.095</ArticleId></ArticleIdList></PubmedData></pubmed><affiliations><list><country><li>Allemagne</li></country><region><li>Berlin</li><li>District de Kassel</li><li>Hesse (Land)</li></region><settlement><li>Berlin</li><li>Cassel (Hesse)</li></settlement></list><tree><country name="Allemagne"><noRegion><name sortKey="Falk, Sandy" sort="Falk, Sandy" uniqKey="Falk S" first="Sandy" last="Falk">Sandy Falk</name></noRegion><name sortKey="Brunn, Hubertus" sort="Brunn, Hubertus" uniqKey="Brunn H" first="Hubertus" last="Brunn">Hubertus Brunn</name><name sortKey="Fliedner, Annette" sort="Fliedner, Annette" uniqKey="Fliedner A" first="Annette" last="Fliedner">Annette Fliedner</name><name sortKey="Koschorreck, Jan" sort="Koschorreck, Jan" uniqKey="Koschorreck J" first="Jan" last="Koschorreck">Jan Koschorreck</name><name sortKey="Rudel, Heinz" sort="Rudel, Heinz" uniqKey="Rudel H" first="Heinz" last="Rüdel">Heinz Rüdel</name><name sortKey="Stahl, Thorsten" sort="Stahl, Thorsten" uniqKey="Stahl T" first="Thorsten" last="Stahl">Thorsten Stahl</name><name sortKey="Tarricone, Kathrin" sort="Tarricone, Kathrin" uniqKey="Tarricone K" first="Kathrin" last="Tarricone">Kathrin Tarricone</name></country></tree></affiliations></record>Pour manipuler ce document sous Unix (Dilib)
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