Comparison of mussels and semi-permeable membrane devices as intertidal monitors of polycyclic aromatic hydrocarbons at oil spill sites
Side-by-side comparisons of polycyclic aromatic hydrocarbon (PAH) concentrations in resident blue mussels ( Mytilus trossulus) and in semi-permeable membrane devices (SPMDs) were made at four sites in Prince William Sound, Alaska. SPMDs were deployed for ∼30 days on the surface of the beach sediment...
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description | Side-by-side comparisons of polycyclic aromatic hydrocarbon (PAH) concentrations in resident blue mussels (
Mytilus trossulus) and in semi-permeable membrane devices (SPMDs) were made at four sites in Prince William Sound, Alaska. SPMDs were deployed for ∼30
days on the surface of the beach sediment at three tidal elevations on each shore and in 0.5
m deep open pits in the middle intertidal zone. Total PAH (TPAH) concentrations in mussels and in SPMDs were correlated, but the PAH compositions were different. The lower molecular weight PAH were relatively more abundant in the SPMDs than in the mussels at oiled and HA sites. TPAH concentrations in SPMDs deployed in pits and mussels collected adjacent to those pits at oiled sites were higher than in SPMDs and mussels from non-pitted SPMD locations ∼3–15
m from the pits. Pitting released buried oil making its PAH bioavailable. SPMDs deployed in the supratidal zone (+4.0
m tidal elevation) were exposed to atmospheric contaminants for a large fraction of the deployment time and accumulated primarily pyrogenic (combustion-sourced) PAH from the atmosphere. The SPMD strips supplied by the manufacturer contained significant amounts (∼125
ng/strip) of primarily alkylated 2–3 ring PAH. These blank levels make SPMDs unsuitable for shoreline assessments when environmental PAH concentrations are low. Consequently, where available, mussels are recommended for use in assessments of the bioavailability of buried oil residues sequestered in intertidal sediments following an oil spill. Mussels are the preferred monitoring tool when the assessments involve food-chain effects. At locations where the absence of mussels necessitates the use of SPMDs or other passive sampling devices, their limitations need to be carefully considered in the interpretation of results. |
doi_str_mv | 10.1016/j.marpolbul.2005.02.002 |
format | Article |
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Mytilus trossulus) and in semi-permeable membrane devices (SPMDs) were made at four sites in Prince William Sound, Alaska. SPMDs were deployed for ∼30
days on the surface of the beach sediment at three tidal elevations on each shore and in 0.5
m deep open pits in the middle intertidal zone. Total PAH (TPAH) concentrations in mussels and in SPMDs were correlated, but the PAH compositions were different. The lower molecular weight PAH were relatively more abundant in the SPMDs than in the mussels at oiled and HA sites. TPAH concentrations in SPMDs deployed in pits and mussels collected adjacent to those pits at oiled sites were higher than in SPMDs and mussels from non-pitted SPMD locations ∼3–15
m from the pits. Pitting released buried oil making its PAH bioavailable. SPMDs deployed in the supratidal zone (+4.0
m tidal elevation) were exposed to atmospheric contaminants for a large fraction of the deployment time and accumulated primarily pyrogenic (combustion-sourced) PAH from the atmosphere. The SPMD strips supplied by the manufacturer contained significant amounts (∼125
ng/strip) of primarily alkylated 2–3 ring PAH. These blank levels make SPMDs unsuitable for shoreline assessments when environmental PAH concentrations are low. Consequently, where available, mussels are recommended for use in assessments of the bioavailability of buried oil residues sequestered in intertidal sediments following an oil spill. Mussels are the preferred monitoring tool when the assessments involve food-chain effects. At locations where the absence of mussels necessitates the use of SPMDs or other passive sampling devices, their limitations need to be carefully considered in the interpretation of results.</description><identifier>ISSN: 0025-326X</identifier><identifier>EISSN: 1879-3363</identifier><identifier>DOI: 10.1016/j.marpolbul.2005.02.002</identifier><identifier>PMID: 15993141</identifier><identifier>CODEN: MPNBAZ</identifier><language>eng</language><publisher>Oxford: Elsevier Ltd</publisher><subject>Alaska ; Animal, plant and microbial ecology ; Animals ; Applied ecology ; Applied sciences ; Biological and medical sciences ; Bivalvia ; Bivalvia - chemistry ; Bivalvia - metabolism ; Cell Membrane Permeability ; Disasters ; Earth sciences ; Earth, ocean, space ; Ecotoxicology, biological effects of pollution ; Engineering and environment geology. Geothermics ; Environmental Monitoring ; Exact sciences and technology ; Fundamental and applied biological sciences. Psychology ; Marine and brackish environment ; Mussels ; Mytilus edulis ; Mytilus trossulus ; Natural water pollution ; Oceans and Seas ; Oil spills ; PAHs ; Petroleum - analysis ; Petroleum - toxicity ; Pollution ; Pollution, environment geology ; Polycyclic Aromatic Hydrocarbons - analysis ; Polycyclic Aromatic Hydrocarbons - toxicity ; Seawaters, estuaries ; SPMD ; Water Pollutants, Chemical - analysis ; Water Pollutants, Chemical - toxicity ; Water treatment and pollution</subject><ispartof>Marine pollution bulletin, 2005-07, Vol.50 (7), p.740-750</ispartof><rights>2005 Elsevier Ltd</rights><rights>2005 INIST-CNRS</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c461t-78bac7472e50ce1645093c50a77ad0eb7bd82cc348307ecf82bc75dc1b9934053</citedby><cites>FETCH-LOGICAL-c461t-78bac7472e50ce1645093c50a77ad0eb7bd82cc348307ecf82bc75dc1b9934053</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktohtml>$$Uhttps://www.sciencedirect.com/science/article/pii/S0025326X05000536$$EHTML$$P50$$Gelsevier$$H</linktohtml><link.rule.ids>314,776,780,3537,27901,27902,65306</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=16926625$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/15993141$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Boehm, Paul D.</creatorcontrib><creatorcontrib>Page, David S.</creatorcontrib><creatorcontrib>Brown, John S.</creatorcontrib><creatorcontrib>Neff, Jerry M.</creatorcontrib><creatorcontrib>Edward Bence, A.</creatorcontrib><title>Comparison of mussels and semi-permeable membrane devices as intertidal monitors of polycyclic aromatic hydrocarbons at oil spill sites</title><title>Marine pollution bulletin</title><addtitle>Mar Pollut Bull</addtitle><description>Side-by-side comparisons of polycyclic aromatic hydrocarbon (PAH) concentrations in resident blue mussels (
Mytilus trossulus) and in semi-permeable membrane devices (SPMDs) were made at four sites in Prince William Sound, Alaska. SPMDs were deployed for ∼30
days on the surface of the beach sediment at three tidal elevations on each shore and in 0.5
m deep open pits in the middle intertidal zone. Total PAH (TPAH) concentrations in mussels and in SPMDs were correlated, but the PAH compositions were different. The lower molecular weight PAH were relatively more abundant in the SPMDs than in the mussels at oiled and HA sites. TPAH concentrations in SPMDs deployed in pits and mussels collected adjacent to those pits at oiled sites were higher than in SPMDs and mussels from non-pitted SPMD locations ∼3–15
m from the pits. Pitting released buried oil making its PAH bioavailable. SPMDs deployed in the supratidal zone (+4.0
m tidal elevation) were exposed to atmospheric contaminants for a large fraction of the deployment time and accumulated primarily pyrogenic (combustion-sourced) PAH from the atmosphere. The SPMD strips supplied by the manufacturer contained significant amounts (∼125
ng/strip) of primarily alkylated 2–3 ring PAH. These blank levels make SPMDs unsuitable for shoreline assessments when environmental PAH concentrations are low. Consequently, where available, mussels are recommended for use in assessments of the bioavailability of buried oil residues sequestered in intertidal sediments following an oil spill. Mussels are the preferred monitoring tool when the assessments involve food-chain effects. At locations where the absence of mussels necessitates the use of SPMDs or other passive sampling devices, their limitations need to be carefully considered in the interpretation of results.</description><subject>Alaska</subject><subject>Animal, plant and microbial ecology</subject><subject>Animals</subject><subject>Applied ecology</subject><subject>Applied sciences</subject><subject>Biological and medical sciences</subject><subject>Bivalvia</subject><subject>Bivalvia - chemistry</subject><subject>Bivalvia - metabolism</subject><subject>Cell Membrane Permeability</subject><subject>Disasters</subject><subject>Earth sciences</subject><subject>Earth, ocean, space</subject><subject>Ecotoxicology, biological effects of pollution</subject><subject>Engineering and environment geology. Geothermics</subject><subject>Environmental Monitoring</subject><subject>Exact sciences and technology</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>Marine and brackish environment</subject><subject>Mussels</subject><subject>Mytilus edulis</subject><subject>Mytilus trossulus</subject><subject>Natural water pollution</subject><subject>Oceans and Seas</subject><subject>Oil spills</subject><subject>PAHs</subject><subject>Petroleum - analysis</subject><subject>Petroleum - toxicity</subject><subject>Pollution</subject><subject>Pollution, environment geology</subject><subject>Polycyclic Aromatic Hydrocarbons - analysis</subject><subject>Polycyclic Aromatic Hydrocarbons - toxicity</subject><subject>Seawaters, estuaries</subject><subject>SPMD</subject><subject>Water Pollutants, Chemical - analysis</subject><subject>Water Pollutants, Chemical - toxicity</subject><subject>Water treatment and pollution</subject><issn>0025-326X</issn><issn>1879-3363</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2005</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNqFkcuOFCEUQInROO3oLygb3VUJ1IOq5aQzPpJJ3GjijsDlVqQDRQlVJv0F_rZUuuMsZwPk5twXh5B3nNWc8f7jqQ46LdGbzdeCsa5momZMPCMHPsixapq-eU4OJdJVjeh_3pBXOZ8YY1JI_pLc8G4cG97yA_l7jGHRyeU40zjRsOWMPlM9W5oxuGrBFFAbjzRgMEnPSC3-cYCFydTNK6bVWe1piLNbY8p7lTLYGc7gHVCdYtBrefw62xRBJxPnkrrS6DzNi_PldCvm1-TFpH3GN9f7lvz4dP_9-KV6-Pb56_HuoYK252slB6NBtlJgxwB533ZsbKBjWkptGRpp7CAAmnZomESYBmFAdha4KQu3rGtuyYdL3SXF3xvmVQWXAb0vm8UtK74XH9nwNNjK0lzyAsoLCCnmnHBSS3LFzllxpnZZ6qT-y1K7LMWEKmpK5ttri80EtI95VzsFeH8FdAbtp_L94PIj14-i78W-1N2FK-qKHEwqg8MZ0LqEsCob3ZPD_ANU5bpb</recordid><startdate>20050701</startdate><enddate>20050701</enddate><creator>Boehm, Paul D.</creator><creator>Page, David S.</creator><creator>Brown, John S.</creator><creator>Neff, Jerry M.</creator><creator>Edward Bence, A.</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>7QH</scope><scope>7TN</scope><scope>7TV</scope><scope>7U7</scope><scope>7UA</scope><scope>F1W</scope><scope>H95</scope><scope>H97</scope><scope>L.G</scope></search><sort><creationdate>20050701</creationdate><title>Comparison of mussels and semi-permeable membrane devices as intertidal monitors of polycyclic aromatic hydrocarbons at oil spill sites</title><author>Boehm, Paul D. ; Page, David S. ; Brown, John S. ; Neff, Jerry M. ; Edward Bence, A.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c461t-78bac7472e50ce1645093c50a77ad0eb7bd82cc348307ecf82bc75dc1b9934053</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2005</creationdate><topic>Alaska</topic><topic>Animal, plant and microbial ecology</topic><topic>Animals</topic><topic>Applied ecology</topic><topic>Applied sciences</topic><topic>Biological and medical sciences</topic><topic>Bivalvia</topic><topic>Bivalvia - chemistry</topic><topic>Bivalvia - metabolism</topic><topic>Cell Membrane Permeability</topic><topic>Disasters</topic><topic>Earth sciences</topic><topic>Earth, ocean, space</topic><topic>Ecotoxicology, biological effects of pollution</topic><topic>Engineering and environment geology. Geothermics</topic><topic>Environmental Monitoring</topic><topic>Exact sciences and technology</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>Marine and brackish environment</topic><topic>Mussels</topic><topic>Mytilus edulis</topic><topic>Mytilus trossulus</topic><topic>Natural water pollution</topic><topic>Oceans and Seas</topic><topic>Oil spills</topic><topic>PAHs</topic><topic>Petroleum - analysis</topic><topic>Petroleum - toxicity</topic><topic>Pollution</topic><topic>Pollution, environment geology</topic><topic>Polycyclic Aromatic Hydrocarbons - analysis</topic><topic>Polycyclic Aromatic Hydrocarbons - toxicity</topic><topic>Seawaters, estuaries</topic><topic>SPMD</topic><topic>Water Pollutants, Chemical - analysis</topic><topic>Water Pollutants, Chemical - toxicity</topic><topic>Water treatment and pollution</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Boehm, Paul D.</creatorcontrib><creatorcontrib>Page, David S.</creatorcontrib><creatorcontrib>Brown, John S.</creatorcontrib><creatorcontrib>Neff, Jerry M.</creatorcontrib><creatorcontrib>Edward Bence, A.</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>Aqualine</collection><collection>Oceanic Abstracts</collection><collection>Pollution Abstracts</collection><collection>Toxicology Abstracts</collection><collection>Water Resources Abstracts</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 1: Biological Sciences & Living Resources</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 3: Aquatic Pollution & Environmental Quality</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><jtitle>Marine pollution bulletin</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Boehm, Paul D.</au><au>Page, David S.</au><au>Brown, John S.</au><au>Neff, Jerry M.</au><au>Edward Bence, A.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Comparison of mussels and semi-permeable membrane devices as intertidal monitors of polycyclic aromatic hydrocarbons at oil spill sites</atitle><jtitle>Marine pollution bulletin</jtitle><addtitle>Mar Pollut Bull</addtitle><date>2005-07-01</date><risdate>2005</risdate><volume>50</volume><issue>7</issue><spage>740</spage><epage>750</epage><pages>740-750</pages><issn>0025-326X</issn><eissn>1879-3363</eissn><coden>MPNBAZ</coden><abstract>Side-by-side comparisons of polycyclic aromatic hydrocarbon (PAH) concentrations in resident blue mussels (
Mytilus trossulus) and in semi-permeable membrane devices (SPMDs) were made at four sites in Prince William Sound, Alaska. SPMDs were deployed for ∼30
days on the surface of the beach sediment at three tidal elevations on each shore and in 0.5
m deep open pits in the middle intertidal zone. Total PAH (TPAH) concentrations in mussels and in SPMDs were correlated, but the PAH compositions were different. The lower molecular weight PAH were relatively more abundant in the SPMDs than in the mussels at oiled and HA sites. TPAH concentrations in SPMDs deployed in pits and mussels collected adjacent to those pits at oiled sites were higher than in SPMDs and mussels from non-pitted SPMD locations ∼3–15
m from the pits. Pitting released buried oil making its PAH bioavailable. SPMDs deployed in the supratidal zone (+4.0
m tidal elevation) were exposed to atmospheric contaminants for a large fraction of the deployment time and accumulated primarily pyrogenic (combustion-sourced) PAH from the atmosphere. The SPMD strips supplied by the manufacturer contained significant amounts (∼125
ng/strip) of primarily alkylated 2–3 ring PAH. These blank levels make SPMDs unsuitable for shoreline assessments when environmental PAH concentrations are low. Consequently, where available, mussels are recommended for use in assessments of the bioavailability of buried oil residues sequestered in intertidal sediments following an oil spill. Mussels are the preferred monitoring tool when the assessments involve food-chain effects. At locations where the absence of mussels necessitates the use of SPMDs or other passive sampling devices, their limitations need to be carefully considered in the interpretation of results.</abstract><cop>Oxford</cop><pub>Elsevier Ltd</pub><pmid>15993141</pmid><doi>10.1016/j.marpolbul.2005.02.002</doi><tpages>11</tpages></addata></record> |
fulltext | fulltext |
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ispartof | Marine pollution bulletin, 2005-07, Vol.50 (7), p.740-750 |
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source | MEDLINE; Elsevier ScienceDirect Journals |
subjects | Alaska Animal, plant and microbial ecology Animals Applied ecology Applied sciences Biological and medical sciences Bivalvia Bivalvia - chemistry Bivalvia - metabolism Cell Membrane Permeability Disasters Earth sciences Earth, ocean, space Ecotoxicology, biological effects of pollution Engineering and environment geology. Geothermics Environmental Monitoring Exact sciences and technology Fundamental and applied biological sciences. Psychology Marine and brackish environment Mussels Mytilus edulis Mytilus trossulus Natural water pollution Oceans and Seas Oil spills PAHs Petroleum - analysis Petroleum - toxicity Pollution Pollution, environment geology Polycyclic Aromatic Hydrocarbons - analysis Polycyclic Aromatic Hydrocarbons - toxicity Seawaters, estuaries SPMD Water Pollutants, Chemical - analysis Water Pollutants, Chemical - toxicity Water treatment and pollution |
title | Comparison of mussels and semi-permeable membrane devices as intertidal monitors of polycyclic aromatic hydrocarbons at oil spill sites |
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