Concentrations and time trends of polybrominated diphenyl ethers (PBDEs) and polychlorinated biphenyls (PCBs) in aquatic bird eggs from San Francisco Bay, CA 2000–2003
Concentrations of polybrominated diphenyl ethers (PBDEs) and polychlorinated biphenyls (PCBs) were measured in 169 avian eggs. We analyzed randomly collected eggs of two species of piscivorous birds: Caspian tern ( Sterna caspia) ( n = 78) and Forster’s tern (Sterna forsteri) ( n = 76). We also anal...
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description | Concentrations of polybrominated diphenyl ethers (PBDEs) and polychlorinated biphenyls (PCBs) were measured in 169 avian eggs. We analyzed randomly collected eggs of two species of piscivorous birds: Caspian tern (
Sterna caspia) (
n
=
78) and Forster’s tern
(Sterna forsteri) (
n
=
76). We also analyzed fail-to-hatch eggs from two species protected under the Federal Endangered Species Act of 1973, that breed in the San Francisco Bay region: the piscivorous California Least tern (
Sterna antillarum brownii) (
n
=
11) and the omnivorous California Clapper rail (
Rallus longirostris obsoletus) (
n
=
4). San Francisco Bay eggs were collected annually for four years (2000–2003), and additional 20 eggs were collected and analyzed from Gray’s Harbor, Washington in 2001. Geometric mean PBDE concentrations did not significantly differ in the three tern species, but concentrations in eggs from the fail to hatch California Clapper rail eggs were significantly lower than those found in the randomly collected tern eggs. Median concentrations of ∑PBDEs in Caspian tern eggs for 2000–2003 were 2410, 4730, 3720 and 2880
ng/g lipid weight (lw), respectively, in Forster’s terns 1820, 4380, 5460 and 3600
ng/g lw, respectively, and in California Least terns for 2001 and 2002 were 5060 and 5170
ng/g
lw, respectively. In contrast, median ∑PBDEs concentration in California Clapper rail eggs for 2001 was 379
ng/g
lw. Five PBDEs were the major congeners found and decreased in the order BDE-47, -99, -100, -153, and -154. BDE-32, -28, -71, -66, -85, -183 were less prevalent, minor congeners, as was BDE-209, which was measured in a subset of samples. PBDE concentrations in bird eggs from San Francisco Bay were site related. There was no significant difference in PBDE concentrations in Caspian tern eggs from San Francisco Bay and Gray’s Harbor, WA. Average PBDE concentrations in eggs did not significantly increase over the period 2000–2003. |
doi_str_mv | 10.1016/j.chemosphere.2007.04.092 |
format | Article |
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Sterna caspia) (
n
=
78) and Forster’s tern
(Sterna forsteri) (
n
=
76). We also analyzed fail-to-hatch eggs from two species protected under the Federal Endangered Species Act of 1973, that breed in the San Francisco Bay region: the piscivorous California Least tern (
Sterna antillarum brownii) (
n
=
11) and the omnivorous California Clapper rail (
Rallus longirostris obsoletus) (
n
=
4). San Francisco Bay eggs were collected annually for four years (2000–2003), and additional 20 eggs were collected and analyzed from Gray’s Harbor, Washington in 2001. Geometric mean PBDE concentrations did not significantly differ in the three tern species, but concentrations in eggs from the fail to hatch California Clapper rail eggs were significantly lower than those found in the randomly collected tern eggs. Median concentrations of ∑PBDEs in Caspian tern eggs for 2000–2003 were 2410, 4730, 3720 and 2880
ng/g lipid weight (lw), respectively, in Forster’s terns 1820, 4380, 5460 and 3600
ng/g lw, respectively, and in California Least terns for 2001 and 2002 were 5060 and 5170
ng/g
lw, respectively. In contrast, median ∑PBDEs concentration in California Clapper rail eggs for 2001 was 379
ng/g
lw. Five PBDEs were the major congeners found and decreased in the order BDE-47, -99, -100, -153, and -154. BDE-32, -28, -71, -66, -85, -183 were less prevalent, minor congeners, as was BDE-209, which was measured in a subset of samples. PBDE concentrations in bird eggs from San Francisco Bay were site related. There was no significant difference in PBDE concentrations in Caspian tern eggs from San Francisco Bay and Gray’s Harbor, WA. Average PBDE concentrations in eggs did not significantly increase over the period 2000–2003.</description><identifier>ISSN: 0045-6535</identifier><identifier>EISSN: 1879-1298</identifier><identifier>DOI: 10.1016/j.chemosphere.2007.04.092</identifier><identifier>PMID: 18466953</identifier><identifier>CODEN: CMSHAF</identifier><language>eng</language><publisher>Kidlington: Elsevier Ltd</publisher><subject>Animal, plant and microbial ecology ; Animals ; Applied ecology ; Aves ; Biological and medical sciences ; Bird eggs ; Birds - anatomy & histology ; Complex Mixtures - chemistry ; Ecotoxicology, biological effects of pollution ; Environmental Monitoring - statistics & numerical data ; Female ; Fishes ; Fundamental and applied biological sciences. Psychology ; General aspects ; Halogenated Diphenyl Ethers ; Humans ; Marine ; Marine Biology ; Ovum - chemistry ; Phenyl Ethers - analysis ; Phenyl Ethers - chemistry ; Polybrominated Biphenyls - analysis ; Polybrominated Biphenyls - chemistry ; Polybrominated diphenylethers (PBDEs) ; Polychlorinated biphenyls (PCBs) ; Polychlorinated Biphenyls - analysis ; Polychlorinated Biphenyls - chemistry ; Rallus longirostris obsoletus ; San Francisco ; San Francisco Bay ; Species Specificity ; Sterna antillarum ; Sterna caspia ; Sterna forsteri ; Tern eggs ; Time Factors ; Time trend ; Vertebrates: general zoology, morphology, phylogeny, systematics, cytogenetics, geographical distribution ; Water</subject><ispartof>Chemosphere (Oxford), 2008-08, Vol.73 (1), p.S201-S209</ispartof><rights>2008 Elsevier Ltd</rights><rights>2009 INIST-CNRS</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c467t-7534227c69e5b5b0e8f6df778d8659a285f98fdb6dab2a8c92d5d62dfe5f9aea3</citedby><cites>FETCH-LOGICAL-c467t-7534227c69e5b5b0e8f6df778d8659a285f98fdb6dab2a8c92d5d62dfe5f9aea3</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktohtml>$$Uhttps://dx.doi.org/10.1016/j.chemosphere.2007.04.092$$EHTML$$P50$$Gelsevier$$H</linktohtml><link.rule.ids>309,310,314,777,781,786,787,3538,23912,23913,25122,27906,27907,45977</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=20738678$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/18466953$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>She, Jianwen</creatorcontrib><creatorcontrib>Holden, Arthur</creatorcontrib><creatorcontrib>Adelsbach, Terrence L.</creatorcontrib><creatorcontrib>Tanner, Manon</creatorcontrib><creatorcontrib>Schwarzbach, Steven E.</creatorcontrib><creatorcontrib>Yee, Julie L</creatorcontrib><creatorcontrib>Hooper, Kim</creatorcontrib><title>Concentrations and time trends of polybrominated diphenyl ethers (PBDEs) and polychlorinated biphenyls (PCBs) in aquatic bird eggs from San Francisco Bay, CA 2000–2003</title><title>Chemosphere (Oxford)</title><addtitle>Chemosphere</addtitle><description>Concentrations of polybrominated diphenyl ethers (PBDEs) and polychlorinated biphenyls (PCBs) were measured in 169 avian eggs. We analyzed randomly collected eggs of two species of piscivorous birds: Caspian tern (
Sterna caspia) (
n
=
78) and Forster’s tern
(Sterna forsteri) (
n
=
76). We also analyzed fail-to-hatch eggs from two species protected under the Federal Endangered Species Act of 1973, that breed in the San Francisco Bay region: the piscivorous California Least tern (
Sterna antillarum brownii) (
n
=
11) and the omnivorous California Clapper rail (
Rallus longirostris obsoletus) (
n
=
4). San Francisco Bay eggs were collected annually for four years (2000–2003), and additional 20 eggs were collected and analyzed from Gray’s Harbor, Washington in 2001. Geometric mean PBDE concentrations did not significantly differ in the three tern species, but concentrations in eggs from the fail to hatch California Clapper rail eggs were significantly lower than those found in the randomly collected tern eggs. Median concentrations of ∑PBDEs in Caspian tern eggs for 2000–2003 were 2410, 4730, 3720 and 2880
ng/g lipid weight (lw), respectively, in Forster’s terns 1820, 4380, 5460 and 3600
ng/g lw, respectively, and in California Least terns for 2001 and 2002 were 5060 and 5170
ng/g
lw, respectively. In contrast, median ∑PBDEs concentration in California Clapper rail eggs for 2001 was 379
ng/g
lw. Five PBDEs were the major congeners found and decreased in the order BDE-47, -99, -100, -153, and -154. BDE-32, -28, -71, -66, -85, -183 were less prevalent, minor congeners, as was BDE-209, which was measured in a subset of samples. PBDE concentrations in bird eggs from San Francisco Bay were site related. There was no significant difference in PBDE concentrations in Caspian tern eggs from San Francisco Bay and Gray’s Harbor, WA. Average PBDE concentrations in eggs did not significantly increase over the period 2000–2003.</description><subject>Animal, plant and microbial ecology</subject><subject>Animals</subject><subject>Applied ecology</subject><subject>Aves</subject><subject>Biological and medical sciences</subject><subject>Bird eggs</subject><subject>Birds - anatomy & histology</subject><subject>Complex Mixtures - chemistry</subject><subject>Ecotoxicology, biological effects of pollution</subject><subject>Environmental Monitoring - statistics & numerical data</subject><subject>Female</subject><subject>Fishes</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>General aspects</subject><subject>Halogenated Diphenyl Ethers</subject><subject>Humans</subject><subject>Marine</subject><subject>Marine Biology</subject><subject>Ovum - chemistry</subject><subject>Phenyl Ethers - analysis</subject><subject>Phenyl Ethers - chemistry</subject><subject>Polybrominated Biphenyls - analysis</subject><subject>Polybrominated Biphenyls - chemistry</subject><subject>Polybrominated diphenylethers (PBDEs)</subject><subject>Polychlorinated biphenyls (PCBs)</subject><subject>Polychlorinated Biphenyls - analysis</subject><subject>Polychlorinated Biphenyls - chemistry</subject><subject>Rallus longirostris obsoletus</subject><subject>San Francisco</subject><subject>San Francisco Bay</subject><subject>Species Specificity</subject><subject>Sterna antillarum</subject><subject>Sterna caspia</subject><subject>Sterna forsteri</subject><subject>Tern eggs</subject><subject>Time Factors</subject><subject>Time trend</subject><subject>Vertebrates: general zoology, morphology, phylogeny, systematics, cytogenetics, geographical distribution</subject><subject>Water</subject><issn>0045-6535</issn><issn>1879-1298</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2008</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNqNkUGO1DAQRS0EYpqBKyCzAIFEguPEjr2cDjOANBJIwNpy7Mq0W4ndY6eRescdOAXX4iS46QjYwaoW9X79qvoIPalIWZGKv9qWZgNTSLsNRCgpIW1JmpJIegetKtHKoqJS3EUrQhpWcFazM_QgpS0hWczkfXRWiYZzyeoV-t4Fb8DPUc8u-IS1t3h2E-A5grcJhwHvwnjoY5ic1zNYbF229YcRw5ztE37-Yf36Mr34pTyiZjOGuLD9wh6pbp0h57G-3Wcvk3vRYri5SXjIw_FH7fFV1N64ZAJe68NL3F3gfBv58fVbLvVDdG_QY4JHSz1Hn68uP3Vvi-v3b951F9eFaXg7Fy2rG0pbwyWwnvUExMDt0LbCiny7poINUgy251b3VAsjqWWWUztAbmjQ9Tl6dpq7i-F2D2lWU14JxlF7CPukKtmIqq7Jv8FGMMk5zaA8gSaGlCIMahfdpONBVUQdA1Vb9Veg6hioIo3KgWbt48Vk309g_yiXBDPwdAF0MnocTi_8zVHS1oK3InPdiYP8uy8OokrGQc7eughmVja4_1jnJ473xss</recordid><startdate>20080801</startdate><enddate>20080801</enddate><creator>She, Jianwen</creator><creator>Holden, Arthur</creator><creator>Adelsbach, Terrence L.</creator><creator>Tanner, Manon</creator><creator>Schwarzbach, Steven E.</creator><creator>Yee, Julie L</creator><creator>Hooper, Kim</creator><general>Elsevier Ltd</general><general>Elsevier</general><scope>IQODW</scope><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7ST</scope><scope>C1K</scope><scope>SOI</scope><scope>7TN</scope><scope>7TV</scope><scope>7U7</scope><scope>F1W</scope><scope>H97</scope><scope>L.G</scope></search><sort><creationdate>20080801</creationdate><title>Concentrations and time trends of polybrominated diphenyl ethers (PBDEs) and polychlorinated biphenyls (PCBs) in aquatic bird eggs from San Francisco Bay, CA 2000–2003</title><author>She, Jianwen ; Holden, Arthur ; Adelsbach, Terrence L. ; Tanner, Manon ; Schwarzbach, Steven E. ; Yee, Julie L ; Hooper, Kim</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c467t-7534227c69e5b5b0e8f6df778d8659a285f98fdb6dab2a8c92d5d62dfe5f9aea3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2008</creationdate><topic>Animal, plant and microbial ecology</topic><topic>Animals</topic><topic>Applied ecology</topic><topic>Aves</topic><topic>Biological and medical sciences</topic><topic>Bird eggs</topic><topic>Birds - anatomy & histology</topic><topic>Complex Mixtures - chemistry</topic><topic>Ecotoxicology, biological effects of pollution</topic><topic>Environmental Monitoring - statistics & numerical data</topic><topic>Female</topic><topic>Fishes</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>General aspects</topic><topic>Halogenated Diphenyl Ethers</topic><topic>Humans</topic><topic>Marine</topic><topic>Marine Biology</topic><topic>Ovum - chemistry</topic><topic>Phenyl Ethers - analysis</topic><topic>Phenyl Ethers - chemistry</topic><topic>Polybrominated Biphenyls - analysis</topic><topic>Polybrominated Biphenyls - chemistry</topic><topic>Polybrominated diphenylethers (PBDEs)</topic><topic>Polychlorinated biphenyls (PCBs)</topic><topic>Polychlorinated Biphenyls - analysis</topic><topic>Polychlorinated Biphenyls - chemistry</topic><topic>Rallus longirostris obsoletus</topic><topic>San Francisco</topic><topic>San Francisco Bay</topic><topic>Species Specificity</topic><topic>Sterna antillarum</topic><topic>Sterna caspia</topic><topic>Sterna forsteri</topic><topic>Tern eggs</topic><topic>Time Factors</topic><topic>Time trend</topic><topic>Vertebrates: general zoology, morphology, phylogeny, systematics, cytogenetics, geographical distribution</topic><topic>Water</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>She, Jianwen</creatorcontrib><creatorcontrib>Holden, Arthur</creatorcontrib><creatorcontrib>Adelsbach, Terrence L.</creatorcontrib><creatorcontrib>Tanner, Manon</creatorcontrib><creatorcontrib>Schwarzbach, Steven E.</creatorcontrib><creatorcontrib>Yee, Julie L</creatorcontrib><creatorcontrib>Hooper, Kim</creatorcontrib><collection>Pascal-Francis</collection><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>Environment Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Environment Abstracts</collection><collection>Oceanic Abstracts</collection><collection>Pollution Abstracts</collection><collection>Toxicology Abstracts</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 3: Aquatic Pollution & Environmental Quality</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><jtitle>Chemosphere (Oxford)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>She, Jianwen</au><au>Holden, Arthur</au><au>Adelsbach, Terrence L.</au><au>Tanner, Manon</au><au>Schwarzbach, Steven E.</au><au>Yee, Julie L</au><au>Hooper, Kim</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Concentrations and time trends of polybrominated diphenyl ethers (PBDEs) and polychlorinated biphenyls (PCBs) in aquatic bird eggs from San Francisco Bay, CA 2000–2003</atitle><jtitle>Chemosphere (Oxford)</jtitle><addtitle>Chemosphere</addtitle><date>2008-08-01</date><risdate>2008</risdate><volume>73</volume><issue>1</issue><spage>S201</spage><epage>S209</epage><pages>S201-S209</pages><issn>0045-6535</issn><eissn>1879-1298</eissn><coden>CMSHAF</coden><abstract>Concentrations of polybrominated diphenyl ethers (PBDEs) and polychlorinated biphenyls (PCBs) were measured in 169 avian eggs. We analyzed randomly collected eggs of two species of piscivorous birds: Caspian tern (
Sterna caspia) (
n
=
78) and Forster’s tern
(Sterna forsteri) (
n
=
76). We also analyzed fail-to-hatch eggs from two species protected under the Federal Endangered Species Act of 1973, that breed in the San Francisco Bay region: the piscivorous California Least tern (
Sterna antillarum brownii) (
n
=
11) and the omnivorous California Clapper rail (
Rallus longirostris obsoletus) (
n
=
4). San Francisco Bay eggs were collected annually for four years (2000–2003), and additional 20 eggs were collected and analyzed from Gray’s Harbor, Washington in 2001. Geometric mean PBDE concentrations did not significantly differ in the three tern species, but concentrations in eggs from the fail to hatch California Clapper rail eggs were significantly lower than those found in the randomly collected tern eggs. Median concentrations of ∑PBDEs in Caspian tern eggs for 2000–2003 were 2410, 4730, 3720 and 2880
ng/g lipid weight (lw), respectively, in Forster’s terns 1820, 4380, 5460 and 3600
ng/g lw, respectively, and in California Least terns for 2001 and 2002 were 5060 and 5170
ng/g
lw, respectively. In contrast, median ∑PBDEs concentration in California Clapper rail eggs for 2001 was 379
ng/g
lw. Five PBDEs were the major congeners found and decreased in the order BDE-47, -99, -100, -153, and -154. BDE-32, -28, -71, -66, -85, -183 were less prevalent, minor congeners, as was BDE-209, which was measured in a subset of samples. PBDE concentrations in bird eggs from San Francisco Bay were site related. There was no significant difference in PBDE concentrations in Caspian tern eggs from San Francisco Bay and Gray’s Harbor, WA. Average PBDE concentrations in eggs did not significantly increase over the period 2000–2003.</abstract><cop>Kidlington</cop><pub>Elsevier Ltd</pub><pmid>18466953</pmid><doi>10.1016/j.chemosphere.2007.04.092</doi></addata></record> |
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source | MEDLINE; Elsevier ScienceDirect Journals |
subjects | Animal, plant and microbial ecology Animals Applied ecology Aves Biological and medical sciences Bird eggs Birds - anatomy & histology Complex Mixtures - chemistry Ecotoxicology, biological effects of pollution Environmental Monitoring - statistics & numerical data Female Fishes Fundamental and applied biological sciences. Psychology General aspects Halogenated Diphenyl Ethers Humans Marine Marine Biology Ovum - chemistry Phenyl Ethers - analysis Phenyl Ethers - chemistry Polybrominated Biphenyls - analysis Polybrominated Biphenyls - chemistry Polybrominated diphenylethers (PBDEs) Polychlorinated biphenyls (PCBs) Polychlorinated Biphenyls - analysis Polychlorinated Biphenyls - chemistry Rallus longirostris obsoletus San Francisco San Francisco Bay Species Specificity Sterna antillarum Sterna caspia Sterna forsteri Tern eggs Time Factors Time trend Vertebrates: general zoology, morphology, phylogeny, systematics, cytogenetics, geographical distribution Water |
title | Concentrations and time trends of polybrominated diphenyl ethers (PBDEs) and polychlorinated biphenyls (PCBs) in aquatic bird eggs from San Francisco Bay, CA 2000–2003 |
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