Biomagnification factors (fish to osprey eggs from Willamette River, Oregon, U.S.A.) for PCDDS, PCDFS, PCBS and OC pesticides

A migratory population of 78 pairs of Osprey (Pandion haliaetus) nesting along the Willamette River in western Oregon was studied in 1993. The study was designed to determine contaminant concentrations in eggs, contaminant concentrations in fish species predominant in the Ospreys diet, and Biomagnif...

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Veröffentlicht in:Environmental monitoring and assessment 2003-06, Vol.84 (3), p.275-315
Hauptverfasser: HENNY, Charles J, KAISER, James L, GROVE, Robert A, BENTLEY, V. Raymond, ELLIOTT, John E
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container_start_page 275
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creator HENNY, Charles J
KAISER, James L
GROVE, Robert A
BENTLEY, V. Raymond
ELLIOTT, John E
description A migratory population of 78 pairs of Osprey (Pandion haliaetus) nesting along the Willamette River in western Oregon was studied in 1993. The study was designed to determine contaminant concentrations in eggs, contaminant concentrations in fish species predominant in the Ospreys diet, and Biomagnification Factors (BMFs) of contaminants from fish species eaten to Osprey eggs. Ten Osprey eggs and 25 composite samples of fish (3 species) were used to evaluate organochlorine (OC) pesticides, polychlorinated biphenyls (PCBs), polychlorinated dibenzo-p-dioxins (PCDDs), and polychlorinated dibenzofurans (PCDFs). Mercury was also analyzed in fish. Geometric mean residues in Osprey eggs were judged low, e.g., DDE 2.3 microg g(-1) wet weight (ww), sigma PCBs 0.69 microg g(-1), 2,3,7,8-TCDD 2.3 ng kg(-1), and generally well below known threshold values for adverse effects on productivity, and the population was increasing. Osprey egg residue data presented by River Mile (RM) are discussed, e.g., higher PCDDs were generally found immediately downstream of paper mills and eggs from the Willamette River had significantly elevated PCBs and PCDDs compared to reference eggs collected nearby in the Cascade Mountains. Prey remains at nest sites indicated that the Largescale Sucker (Catostomus macrocheilus) and Northern Pikeminnow (Ptychocheilus oregonensis) accounted for an estimated 90.1% of the biomass in the Osprey diet, and composite samples of these two species were collected from different sampling sites throughout the study area for contaminant analyses. With the large percentage of the fish biomass in the Osprey diet sampled for contaminants (and fish eaten by Ospreys similar in size to those chemically analyzed), and fish contaminant concentrations weighted by biomass intake, a mean BMF was estimated from fish to Osprey eggs for the large series of contaminants. BMFs ranged from no biomagnification (0.42) for 2,3,7,8-TCDF to 174 for OCDD. Our findings for the migratory Osprey were compared to BMFs for the resident Herring Gull (Larus argentatus), and differences are discussed. We believe a BMF approach provides some basic understanding of relationships between contaminant burdens in prey species of fish-eating birds and contaminants incorporated into their eggs, and may prove useful in understanding sources of contaminants in migratory species although additional studies are needed.
doi_str_mv 10.1023/A:1023396815092
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Geometric mean residues in Osprey eggs were judged low, e.g., DDE 2.3 microg g(-1) wet weight (ww), sigma PCBs 0.69 microg g(-1), 2,3,7,8-TCDD 2.3 ng kg(-1), and generally well below known threshold values for adverse effects on productivity, and the population was increasing. Osprey egg residue data presented by River Mile (RM) are discussed, e.g., higher PCDDs were generally found immediately downstream of paper mills and eggs from the Willamette River had significantly elevated PCBs and PCDDs compared to reference eggs collected nearby in the Cascade Mountains. Prey remains at nest sites indicated that the Largescale Sucker (Catostomus macrocheilus) and Northern Pikeminnow (Ptychocheilus oregonensis) accounted for an estimated 90.1% of the biomass in the Osprey diet, and composite samples of these two species were collected from different sampling sites throughout the study area for contaminant analyses. With the large percentage of the fish biomass in the Osprey diet sampled for contaminants (and fish eaten by Ospreys similar in size to those chemically analyzed), and fish contaminant concentrations weighted by biomass intake, a mean BMF was estimated from fish to Osprey eggs for the large series of contaminants. BMFs ranged from no biomagnification (0.42) for 2,3,7,8-TCDF to 174 for OCDD. Our findings for the migratory Osprey were compared to BMFs for the resident Herring Gull (Larus argentatus), and differences are discussed. 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Psychology ; Industrial Waste ; Larus argentatus ; Mercury ; Mercury - analysis ; Nesting ; Nitrous oxide ; Oregon ; Organic compounds ; Pandion haliaetus ; PCB ; PCDD ; PCDF ; Pesticides ; Pesticides - isolation &amp; purification ; Pesticides - toxicity ; Polychlorinated biphenyls ; Polychlorinated Biphenyls - isolation &amp; purification ; Polychlorinated Biphenyls - toxicity ; Polychlorinated dibenzodioxins ; Polychlorinated dibenzofurans ; Predation ; Prey ; Ptychocheilus oregonensis ; Raptors - physiology ; Reproduction - drug effects ; Rivers ; Water Pollutants, Chemical - analysis ; Water Pollutants, Chemical - toxicity</subject><ispartof>Environmental monitoring and assessment, 2003-06, Vol.84 (3), p.275-315</ispartof><rights>2003 INIST-CNRS</rights><rights>Kluwer Academic Publishers 2003</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c372t-211ab3b8a6021aac457581667490397b14043777ece6248a558c22babbe22a6b3</citedby></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,776,780,27901,27902</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&amp;idt=14775226$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/12807265$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>HENNY, Charles J</creatorcontrib><creatorcontrib>KAISER, James L</creatorcontrib><creatorcontrib>GROVE, Robert A</creatorcontrib><creatorcontrib>BENTLEY, V. Raymond</creatorcontrib><creatorcontrib>ELLIOTT, John E</creatorcontrib><title>Biomagnification factors (fish to osprey eggs from Willamette River, Oregon, U.S.A.) for PCDDS, PCDFS, PCBS and OC pesticides</title><title>Environmental monitoring and assessment</title><addtitle>Environ Monit Assess</addtitle><description>A migratory population of 78 pairs of Osprey (Pandion haliaetus) nesting along the Willamette River in western Oregon was studied in 1993. The study was designed to determine contaminant concentrations in eggs, contaminant concentrations in fish species predominant in the Ospreys diet, and Biomagnification Factors (BMFs) of contaminants from fish species eaten to Osprey eggs. Ten Osprey eggs and 25 composite samples of fish (3 species) were used to evaluate organochlorine (OC) pesticides, polychlorinated biphenyls (PCBs), polychlorinated dibenzo-p-dioxins (PCDDs), and polychlorinated dibenzofurans (PCDFs). Mercury was also analyzed in fish. 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With the large percentage of the fish biomass in the Osprey diet sampled for contaminants (and fish eaten by Ospreys similar in size to those chemically analyzed), and fish contaminant concentrations weighted by biomass intake, a mean BMF was estimated from fish to Osprey eggs for the large series of contaminants. BMFs ranged from no biomagnification (0.42) for 2,3,7,8-TCDF to 174 for OCDD. Our findings for the migratory Osprey were compared to BMFs for the resident Herring Gull (Larus argentatus), and differences are discussed. 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Raymond ; ELLIOTT, John E</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c372t-211ab3b8a6021aac457581667490397b14043777ece6248a558c22babbe22a6b3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2003</creationdate><topic>Animal, plant and microbial ecology</topic><topic>Animals</topic><topic>Applied ecology</topic><topic>Bioaccumulation</topic><topic>Biological and medical sciences</topic><topic>Biological magnification</topic><topic>Birds</topic><topic>Catostomus macrocheilus</topic><topic>Contaminants</topic><topic>Cypriniformes - physiology</topic><topic>DDE</topic><topic>Diet</topic><topic>Ecotoxicology, biological effects of pollution</topic><topic>Eggs</topic><topic>Eggs - analysis</topic><topic>Environmental monitoring</topic><topic>Fish</topic><topic>Food Chain</topic><topic>Fresh Water - analysis</topic><topic>Fresh water environment</topic><topic>Freshwater</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>Industrial Waste</topic><topic>Larus argentatus</topic><topic>Mercury</topic><topic>Mercury - analysis</topic><topic>Nesting</topic><topic>Nitrous oxide</topic><topic>Oregon</topic><topic>Organic compounds</topic><topic>Pandion haliaetus</topic><topic>PCB</topic><topic>PCDD</topic><topic>PCDF</topic><topic>Pesticides</topic><topic>Pesticides - isolation &amp; purification</topic><topic>Pesticides - toxicity</topic><topic>Polychlorinated biphenyls</topic><topic>Polychlorinated Biphenyls - isolation &amp; purification</topic><topic>Polychlorinated Biphenyls - toxicity</topic><topic>Polychlorinated dibenzodioxins</topic><topic>Polychlorinated dibenzofurans</topic><topic>Predation</topic><topic>Prey</topic><topic>Ptychocheilus oregonensis</topic><topic>Raptors - physiology</topic><topic>Reproduction - drug effects</topic><topic>Rivers</topic><topic>Water Pollutants, Chemical - analysis</topic><topic>Water Pollutants, Chemical - toxicity</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>HENNY, Charles J</creatorcontrib><creatorcontrib>KAISER, James L</creatorcontrib><creatorcontrib>GROVE, Robert A</creatorcontrib><creatorcontrib>BENTLEY, V. 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Raymond</au><au>ELLIOTT, John E</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Biomagnification factors (fish to osprey eggs from Willamette River, Oregon, U.S.A.) for PCDDS, PCDFS, PCBS and OC pesticides</atitle><jtitle>Environmental monitoring and assessment</jtitle><addtitle>Environ Monit Assess</addtitle><date>2003-06-01</date><risdate>2003</risdate><volume>84</volume><issue>3</issue><spage>275</spage><epage>315</epage><pages>275-315</pages><issn>0167-6369</issn><eissn>1573-2959</eissn><coden>EMASDH</coden><abstract>A migratory population of 78 pairs of Osprey (Pandion haliaetus) nesting along the Willamette River in western Oregon was studied in 1993. The study was designed to determine contaminant concentrations in eggs, contaminant concentrations in fish species predominant in the Ospreys diet, and Biomagnification Factors (BMFs) of contaminants from fish species eaten to Osprey eggs. Ten Osprey eggs and 25 composite samples of fish (3 species) were used to evaluate organochlorine (OC) pesticides, polychlorinated biphenyls (PCBs), polychlorinated dibenzo-p-dioxins (PCDDs), and polychlorinated dibenzofurans (PCDFs). Mercury was also analyzed in fish. Geometric mean residues in Osprey eggs were judged low, e.g., DDE 2.3 microg g(-1) wet weight (ww), sigma PCBs 0.69 microg g(-1), 2,3,7,8-TCDD 2.3 ng kg(-1), and generally well below known threshold values for adverse effects on productivity, and the population was increasing. Osprey egg residue data presented by River Mile (RM) are discussed, e.g., higher PCDDs were generally found immediately downstream of paper mills and eggs from the Willamette River had significantly elevated PCBs and PCDDs compared to reference eggs collected nearby in the Cascade Mountains. Prey remains at nest sites indicated that the Largescale Sucker (Catostomus macrocheilus) and Northern Pikeminnow (Ptychocheilus oregonensis) accounted for an estimated 90.1% of the biomass in the Osprey diet, and composite samples of these two species were collected from different sampling sites throughout the study area for contaminant analyses. With the large percentage of the fish biomass in the Osprey diet sampled for contaminants (and fish eaten by Ospreys similar in size to those chemically analyzed), and fish contaminant concentrations weighted by biomass intake, a mean BMF was estimated from fish to Osprey eggs for the large series of contaminants. BMFs ranged from no biomagnification (0.42) for 2,3,7,8-TCDF to 174 for OCDD. Our findings for the migratory Osprey were compared to BMFs for the resident Herring Gull (Larus argentatus), and differences are discussed. We believe a BMF approach provides some basic understanding of relationships between contaminant burdens in prey species of fish-eating birds and contaminants incorporated into their eggs, and may prove useful in understanding sources of contaminants in migratory species although additional studies are needed.</abstract><cop>Dordrect</cop><pub>Springer</pub><pmid>12807265</pmid><doi>10.1023/A:1023396815092</doi><tpages>41</tpages></addata></record>
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subjects Animal, plant and microbial ecology
Animals
Applied ecology
Bioaccumulation
Biological and medical sciences
Biological magnification
Birds
Catostomus macrocheilus
Contaminants
Cypriniformes - physiology
DDE
Diet
Ecotoxicology, biological effects of pollution
Eggs
Eggs - analysis
Environmental monitoring
Fish
Food Chain
Fresh Water - analysis
Fresh water environment
Freshwater
Fundamental and applied biological sciences. Psychology
Industrial Waste
Larus argentatus
Mercury
Mercury - analysis
Nesting
Nitrous oxide
Oregon
Organic compounds
Pandion haliaetus
PCB
PCDD
PCDF
Pesticides
Pesticides - isolation & purification
Pesticides - toxicity
Polychlorinated biphenyls
Polychlorinated Biphenyls - isolation & purification
Polychlorinated Biphenyls - toxicity
Polychlorinated dibenzodioxins
Polychlorinated dibenzofurans
Predation
Prey
Ptychocheilus oregonensis
Raptors - physiology
Reproduction - drug effects
Rivers
Water Pollutants, Chemical - analysis
Water Pollutants, Chemical - toxicity
title Biomagnification factors (fish to osprey eggs from Willamette River, Oregon, U.S.A.) for PCDDS, PCDFS, PCBS and OC pesticides
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