Monitoring fish contaminant responses to abatement actions: factors that affect recovery.
Identifieur interne : 002D86 ( Main/Exploration ); précédent : 002D85; suivant : 002D87Monitoring fish contaminant responses to abatement actions: factors that affect recovery.
Auteurs : George R. Southworth [États-Unis] ; Mark J. Peterson ; W Kelly Roy ; Teresa J. MathewsSource :
- Environmental management [ 1432-1009 ] ; 2011.
Descripteurs français
- KwdFr :
- Agences gouvernementale américaines (MeSH), Animaux (MeSH), Assainissement et restauration de l'environnement (MeSH), Femelle (MeSH), Mercure (analyse), Mercure (métabolisme), Mercure (toxicité), Mâle (MeSH), Poids (effets des médicaments et des substances chimiques), Poissons (métabolisme), Polluants chimiques de l'eau (analyse), Polluants chimiques de l'eau (métabolisme), Polluants chimiques de l'eau (toxicité), Pollution chimique de l'eau (statistiques et données numériques), Polychlorobiphényles (analyse), Polychlorobiphényles (métabolisme), Polychlorobiphényles (toxicité), Saisons (MeSH), Surveillance de l'environnement (méthodes), États-Unis (MeSH).
- MESH :
- analyse : Mercure, Polluants chimiques de l'eau, Polychlorobiphényles.
- effets des médicaments et des substances chimiques : Poids.
- métabolisme : Mercure, Poissons, Polluants chimiques de l'eau, Polychlorobiphényles.
- méthodes : Surveillance de l'environnement.
- statistiques et données numériques : Pollution chimique de l'eau.
- toxicité : Mercure, Polluants chimiques de l'eau, Polychlorobiphényles.
- Agences gouvernementale américaines, Animaux, Assainissement et restauration de l'environnement, Femelle, Mâle, Saisons, États-Unis.
- Wicri :
- geographic : États-Unis.
English descriptors
- KwdEn :
- Animals (MeSH), Body Weight (drug effects), Environmental Monitoring (methods), Environmental Restoration and Remediation (MeSH), Female (MeSH), Fishes (metabolism), Male (MeSH), Mercury (analysis), Mercury (metabolism), Mercury (toxicity), Polychlorinated Biphenyls (analysis), Polychlorinated Biphenyls (metabolism), Polychlorinated Biphenyls (toxicity), Seasons (MeSH), United States (MeSH), United States Government Agencies (MeSH), Water Pollutants, Chemical (analysis), Water Pollutants, Chemical (metabolism), Water Pollutants, Chemical (toxicity), Water Pollution, Chemical (statistics & numerical data).
- MESH :
- chemical , analysis : Mercury, Polychlorinated Biphenyls, Water Pollutants, Chemical.
- chemical , metabolism : Water Pollutants, Chemical.
- chemical , toxicity : Water Pollutants, Chemical.
- geographic : United States.
- drug effects : Body Weight.
- metabolism : Fishes, Mercury, Polychlorinated Biphenyls.
- methods : Environmental Monitoring.
- statistics & numerical data : Water Pollution, Chemical.
- chemical , toxicity : Mercury, Polychlorinated Biphenyls.
- Animals, Environmental Restoration and Remediation, Female, Male, Seasons, United States Government Agencies.
Abstract
Monitoring of contaminant accumulation in fish has been conducted in East Fork Poplar Creek (EFPC) in Oak Ridge, Tennessee since 1985. Bioaccumulation trends are examined over a twenty year period coinciding with major pollution abatement actions by a Department of Energy facility at the stream's headwaters. Although EFPC is enriched in many contaminants relative to other local streams, only polychlorinated biphenyls (PCBs) and mercury (Hg) were found to accumulate in the edible portions of fish to levels of human health concern. Mercury concentrations in redbreast sunfish were found to vary with season of collection, sex and size of individual fish. Over the course of the monitoring, waterborne Hg concentrations were reduced >80%; however, this did not translate into a comparable decrease in Hg bioaccumulation at most sites. Mercury bioaccumulation in fish did respond to decreased inputs in the industrialized headwater reach, but paradoxically increased in the lowermost reach of EFPC. As a result, the downstream pattern of Hg concentration in fish changed from one resembling dilution of a headwater point source in the 1980s to a uniform distribution in the 2000s. The reason for this remains unknown, but is hypothesized to involve changes in the chemical form and reactivity of waterborne Hg associated with the removal of residual chlorine and the addition of suspended particulates to the streamflow. PCB concentrations in fish varied greatly from year-to-year, but always exhibited a pronounced downstream decrease, and appeared to respond to management practices that limited episodic inputs from legacy sources within the facility.
DOI: 10.1007/s00267-011-9637-0
PubMed: 21380788
Affiliations:
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Bioaccumulation trends are examined over a twenty year period coinciding with major pollution abatement actions by a Department of Energy facility at the stream's headwaters. Although EFPC is enriched in many contaminants relative to other local streams, only polychlorinated biphenyls (PCBs) and mercury (Hg) were found to accumulate in the edible portions of fish to levels of human health concern. Mercury concentrations in redbreast sunfish were found to vary with season of collection, sex and size of individual fish. Over the course of the monitoring, waterborne Hg concentrations were reduced >80%; however, this did not translate into a comparable decrease in Hg bioaccumulation at most sites. Mercury bioaccumulation in fish did respond to decreased inputs in the industrialized headwater reach, but paradoxically increased in the lowermost reach of EFPC. As a result, the downstream pattern of Hg concentration in fish changed from one resembling dilution of a headwater point source in the 1980s to a uniform distribution in the 2000s. The reason for this remains unknown, but is hypothesized to involve changes in the chemical form and reactivity of waterborne Hg associated with the removal of residual chlorine and the addition of suspended particulates to the streamflow. PCB concentrations in fish varied greatly from year-to-year, but always exhibited a pronounced downstream decrease, and appeared to respond to management practices that limited episodic inputs from legacy sources within the facility.</div></front></TEI><pubmed><MedlineCitation Status="MEDLINE" Owner="NLM"><PMID Version="1">21380788</PMID><DateCompleted><Year>2011</Year><Month>10</Month><Day>12</Day></DateCompleted><DateRevised><Year>2019</Year><Month>12</Month><Day>10</Day></DateRevised><Article PubModel="Print-Electronic"><Journal><ISSN IssnType="Electronic">1432-1009</ISSN><JournalIssue CitedMedium="Internet"><Volume>47</Volume><Issue>6</Issue><PubDate><Year>2011</Year><Month>Jun</Month></PubDate></JournalIssue><Title>Environmental management</Title><ISOAbbreviation>Environ Manage</ISOAbbreviation></Journal><ArticleTitle>Monitoring fish contaminant responses to abatement actions: factors that affect recovery.</ArticleTitle><Pagination><MedlinePgn>1064-76</MedlinePgn></Pagination><ELocationID EIdType="doi" ValidYN="Y">10.1007/s00267-011-9637-0</ELocationID><Abstract><AbstractText>Monitoring of contaminant accumulation in fish has been conducted in East Fork Poplar Creek (EFPC) in Oak Ridge, Tennessee since 1985. Bioaccumulation trends are examined over a twenty year period coinciding with major pollution abatement actions by a Department of Energy facility at the stream's headwaters. Although EFPC is enriched in many contaminants relative to other local streams, only polychlorinated biphenyls (PCBs) and mercury (Hg) were found to accumulate in the edible portions of fish to levels of human health concern. Mercury concentrations in redbreast sunfish were found to vary with season of collection, sex and size of individual fish. Over the course of the monitoring, waterborne Hg concentrations were reduced >80%; however, this did not translate into a comparable decrease in Hg bioaccumulation at most sites. Mercury bioaccumulation in fish did respond to decreased inputs in the industrialized headwater reach, but paradoxically increased in the lowermost reach of EFPC. As a result, the downstream pattern of Hg concentration in fish changed from one resembling dilution of a headwater point source in the 1980s to a uniform distribution in the 2000s. The reason for this remains unknown, but is hypothesized to involve changes in the chemical form and reactivity of waterborne Hg associated with the removal of residual chlorine and the addition of suspended particulates to the streamflow. PCB concentrations in fish varied greatly from year-to-year, but always exhibited a pronounced downstream decrease, and appeared to respond to management practices that limited episodic inputs from legacy sources within the facility.</AbstractText></Abstract><AuthorList CompleteYN="Y"><Author ValidYN="Y"><LastName>Southworth</LastName><ForeName>George R</ForeName><Initials>GR</Initials><AffiliationInfo><Affiliation>Environmental Sciences Division, Oak Ridge National Laboratory, TN 37831, USA.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Peterson</LastName><ForeName>Mark J</ForeName><Initials>MJ</Initials></Author><Author ValidYN="Y"><LastName>Roy</LastName><ForeName>W Kelly</ForeName><Initials>WK</Initials></Author><Author ValidYN="Y"><LastName>Mathews</LastName><ForeName>Teresa J</ForeName><Initials>TJ</Initials></Author></AuthorList><Language>eng</Language><PublicationTypeList><PublicationType UI="D023362">Evaluation Study</PublicationType><PublicationType 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Mathews</name><name sortKey="Peterson, Mark J" sort="Peterson, Mark J" uniqKey="Peterson M" first="Mark J" last="Peterson">Mark J. Peterson</name><name sortKey="Roy, W Kelly" sort="Roy, W Kelly" uniqKey="Roy W" first="W Kelly" last="Roy">W Kelly Roy</name></noCountry><country name="États-Unis"><region name="Tennessee"><name sortKey="Southworth, George R" sort="Southworth, George R" uniqKey="Southworth G" first="George R" last="Southworth">George R. Southworth</name></region></country></tree></affiliations></record>Pour manipuler ce document sous Unix (Dilib)
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