Overview and comparison of lipid-containing semipermeable membrane devices and oysters (Crassostrea gigas) for assessing organic chemical exposure
We performed 20‐d, flow‐through exposures of lipid‐containing semipermeable membrane devices (SPMDs) and Pacific oysters (Crassostrea gigas) to three concentrations (nominally 10, 100, and 250 ng/L) of a diverse mixture of polycyclic aromatic hydrocarbons (PAHs). Exposure water was seawater free of...
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Veröffentlicht in: | Environmental toxicology and chemistry 2004-07, Vol.23 (7), p.1617-1628 |
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creator | Huckins, James N. Prest, Harry F. Petty, Jimmie D. Lebo, Jon A. Hodgins, Maureen M. Clark, Randal C. Alvarez, David A. Gala, William R. Steen, Alexis Gale, Robert Ingersoll, Christopher G. |
description | We performed 20‐d, flow‐through exposures of lipid‐containing semipermeable membrane devices (SPMDs) and Pacific oysters (Crassostrea gigas) to three concentrations (nominally 10, 100, and 250 ng/L) of a diverse mixture of polycyclic aromatic hydrocarbons (PAHs). Exposure water was seawater free of particulates larger than 0.1 μm. The results of these controlled laboratory studies demonstrated that SPMDs and oysters concentrate the same chemicals but that the relative amounts accumulated are different. For oysters, the 20‐d mean (across treatments) concentration factors (CFs) of test compounds with log Kow ≤ 4.8 were much lower (4.0‐ to 20‐fold lower) than those of the same compounds in SPMDs. In contrast, the 20‐d CFs of PAHs with log Kow ≥ 5.6 in oysters from the low‐level treatment were higher than the corresponding CFs for SPMDs. The CFs of these compounds in oysters from the low‐level treatment ranged from approximately 3.0‐ to 13‐fold higher than those in oysters from the high‐level treatment. This physiologically mediated difference in oyster CFs appears to be linked to active feeding in the low‐level treatment and to apparent toxicity‐induced cessation of feeding (i.e., valve closure) in the high‐level treatment. Because CFs for these compounds in oysters were not independent of exposure concentrations, it follows that tissue levels were not proportional to exposure concentration. However, both sampling approaches have advantages and disadvantages, and the appropriateness of their use depends on the goals of a given study. |
doi_str_mv | 10.1897/03-366 |
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Exposure water was seawater free of particulates larger than 0.1 μm. The results of these controlled laboratory studies demonstrated that SPMDs and oysters concentrate the same chemicals but that the relative amounts accumulated are different. For oysters, the 20‐d mean (across treatments) concentration factors (CFs) of test compounds with log Kow ≤ 4.8 were much lower (4.0‐ to 20‐fold lower) than those of the same compounds in SPMDs. In contrast, the 20‐d CFs of PAHs with log Kow ≥ 5.6 in oysters from the low‐level treatment were higher than the corresponding CFs for SPMDs. The CFs of these compounds in oysters from the low‐level treatment ranged from approximately 3.0‐ to 13‐fold higher than those in oysters from the high‐level treatment. This physiologically mediated difference in oyster CFs appears to be linked to active feeding in the low‐level treatment and to apparent toxicity‐induced cessation of feeding (i.e., valve closure) in the high‐level treatment. Because CFs for these compounds in oysters were not independent of exposure concentrations, it follows that tissue levels were not proportional to exposure concentration. However, both sampling approaches have advantages and disadvantages, and the appropriateness of their use depends on the goals of a given study.</description><identifier>ISSN: 0730-7268</identifier><identifier>EISSN: 1552-8618</identifier><identifier>DOI: 10.1897/03-366</identifier><identifier>PMID: 15230313</identifier><identifier>CODEN: ETOCDK</identifier><language>eng</language><publisher>Hoboken: Wiley Periodicals, Inc</publisher><subject>Animal, plant and microbial ecology ; Animals ; Applied ecology ; Biological and medical sciences ; Crassostrea gigas ; Ecotoxicology, biological effects of pollution ; Environmental Exposure ; Environmental Monitoring - methods ; Equilibrium ; Feeding Behavior ; Fundamental and applied biological sciences. Psychology ; General aspects ; Hydrophobic organic chemicals ; Kinetics ; Lipids - chemistry ; Membranes, Artificial ; Organic Chemicals - analysis ; Ostreidae - metabolism ; Oysters ; Polycyclic Aromatic Hydrocarbons - analysis ; Semipermeable membrane devices ; Specimen Handling ; Water Pollutants, Chemical - toxicity</subject><ispartof>Environmental toxicology and chemistry, 2004-07, Vol.23 (7), p.1617-1628</ispartof><rights>Copyright © 2004 SETAC</rights><rights>2004 INIST-CNRS</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c4476-72f8825a19fdc3bd37df84e933966ea43ec534ccbc048253bc2b3a386970f6543</citedby><cites>FETCH-LOGICAL-c4476-72f8825a19fdc3bd37df84e933966ea43ec534ccbc048253bc2b3a386970f6543</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://onlinelibrary.wiley.com/doi/pdf/10.1897%2F03-366$$EPDF$$P50$$Gwiley$$H</linktopdf><linktohtml>$$Uhttps://onlinelibrary.wiley.com/doi/full/10.1897%2F03-366$$EHTML$$P50$$Gwiley$$H</linktohtml><link.rule.ids>314,776,780,1411,27901,27902,45550,45551</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=15877910$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/15230313$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Huckins, James N.</creatorcontrib><creatorcontrib>Prest, Harry F.</creatorcontrib><creatorcontrib>Petty, Jimmie D.</creatorcontrib><creatorcontrib>Lebo, Jon A.</creatorcontrib><creatorcontrib>Hodgins, Maureen M.</creatorcontrib><creatorcontrib>Clark, Randal C.</creatorcontrib><creatorcontrib>Alvarez, David A.</creatorcontrib><creatorcontrib>Gala, William R.</creatorcontrib><creatorcontrib>Steen, Alexis</creatorcontrib><creatorcontrib>Gale, Robert</creatorcontrib><creatorcontrib>Ingersoll, Christopher G.</creatorcontrib><title>Overview and comparison of lipid-containing semipermeable membrane devices and oysters (Crassostrea gigas) for assessing organic chemical exposure</title><title>Environmental toxicology and chemistry</title><addtitle>Environmental Toxicology and Chemistry</addtitle><description>We performed 20‐d, flow‐through exposures of lipid‐containing semipermeable membrane devices (SPMDs) and Pacific oysters (Crassostrea gigas) to three concentrations (nominally 10, 100, and 250 ng/L) of a diverse mixture of polycyclic aromatic hydrocarbons (PAHs). Exposure water was seawater free of particulates larger than 0.1 μm. The results of these controlled laboratory studies demonstrated that SPMDs and oysters concentrate the same chemicals but that the relative amounts accumulated are different. For oysters, the 20‐d mean (across treatments) concentration factors (CFs) of test compounds with log Kow ≤ 4.8 were much lower (4.0‐ to 20‐fold lower) than those of the same compounds in SPMDs. In contrast, the 20‐d CFs of PAHs with log Kow ≥ 5.6 in oysters from the low‐level treatment were higher than the corresponding CFs for SPMDs. The CFs of these compounds in oysters from the low‐level treatment ranged from approximately 3.0‐ to 13‐fold higher than those in oysters from the high‐level treatment. This physiologically mediated difference in oyster CFs appears to be linked to active feeding in the low‐level treatment and to apparent toxicity‐induced cessation of feeding (i.e., valve closure) in the high‐level treatment. 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Psychology</subject><subject>General aspects</subject><subject>Hydrophobic organic chemicals</subject><subject>Kinetics</subject><subject>Lipids - chemistry</subject><subject>Membranes, Artificial</subject><subject>Organic Chemicals - analysis</subject><subject>Ostreidae - metabolism</subject><subject>Oysters</subject><subject>Polycyclic Aromatic Hydrocarbons - analysis</subject><subject>Semipermeable membrane devices</subject><subject>Specimen Handling</subject><subject>Water Pollutants, Chemical - toxicity</subject><issn>0730-7268</issn><issn>1552-8618</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2004</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNqFkc9u1DAQhyMEokuBR0C-gOAQsDOO7RzRihZQ1Ur8EUfLcSaLIYmDZ3fbfQ2eGC-7KlwQ8mEk65tvNPMriseCvxSm0a84lKDUnWIh6roqjRLmbrHgGnipK2VOigdE3zgXqmma-8WJqCvgIGBR_LzaYtoGvGZu6piP4-xSoDix2LMhzKErfZzWLkxhWjHCMcyYRnTtgGzEsU1uQtbhNnik34a4ozUmYs-XyRFFWid0bBVWjl6wPiaWP5FoL4tp5abgmf-ard4NDG_mSJuED4t7vRsIHx3rafH57M2n5dvy4ur83fL1Reml1Crv1RtT1U40feeh7UB3vZHYADRKoZOAvgbpfeu5zBy0vmrBgVGN5r2qJZwWzw7eOcUfG6S1HQN5HIa8U9yQFUpoLRX8H5Sag8nvFvQpEiXs7ZzC6NLOCm73MVkONseUwSdH46YdsfuDHXPJwNMj4Cjfps939oH-4ozWjeCZEwfuOgy4-8c4m4laVTy7Nd8PLw89IUd1c9vj0nerNOjafrk8tx_eX8JHrs-shF-qy7lx</recordid><startdate>200407</startdate><enddate>200407</enddate><creator>Huckins, James N.</creator><creator>Prest, Harry F.</creator><creator>Petty, Jimmie D.</creator><creator>Lebo, Jon A.</creator><creator>Hodgins, Maureen M.</creator><creator>Clark, Randal C.</creator><creator>Alvarez, David A.</creator><creator>Gala, William R.</creator><creator>Steen, Alexis</creator><creator>Gale, Robert</creator><creator>Ingersoll, Christopher G.</creator><general>Wiley Periodicals, Inc</general><general>SETAC</general><scope>BSCLL</scope><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>7TV</scope><scope>7U7</scope><scope>7UA</scope><scope>F1W</scope><scope>H95</scope><scope>H97</scope><scope>L.G</scope></search><sort><creationdate>200407</creationdate><title>Overview and comparison of lipid-containing semipermeable membrane devices and oysters (Crassostrea gigas) for assessing organic chemical exposure</title><author>Huckins, James N. ; Prest, Harry F. ; Petty, Jimmie D. ; Lebo, Jon A. ; Hodgins, Maureen M. ; Clark, Randal C. ; Alvarez, David A. ; Gala, William R. ; Steen, Alexis ; Gale, Robert ; Ingersoll, Christopher G.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c4476-72f8825a19fdc3bd37df84e933966ea43ec534ccbc048253bc2b3a386970f6543</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2004</creationdate><topic>Animal, plant and microbial ecology</topic><topic>Animals</topic><topic>Applied ecology</topic><topic>Biological and medical sciences</topic><topic>Crassostrea gigas</topic><topic>Ecotoxicology, biological effects of pollution</topic><topic>Environmental Exposure</topic><topic>Environmental Monitoring - methods</topic><topic>Equilibrium</topic><topic>Feeding Behavior</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>General aspects</topic><topic>Hydrophobic organic chemicals</topic><topic>Kinetics</topic><topic>Lipids - chemistry</topic><topic>Membranes, Artificial</topic><topic>Organic Chemicals - analysis</topic><topic>Ostreidae - metabolism</topic><topic>Oysters</topic><topic>Polycyclic Aromatic Hydrocarbons - analysis</topic><topic>Semipermeable membrane devices</topic><topic>Specimen Handling</topic><topic>Water Pollutants, Chemical - toxicity</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Huckins, James N.</creatorcontrib><creatorcontrib>Prest, Harry F.</creatorcontrib><creatorcontrib>Petty, Jimmie D.</creatorcontrib><creatorcontrib>Lebo, Jon A.</creatorcontrib><creatorcontrib>Hodgins, Maureen M.</creatorcontrib><creatorcontrib>Clark, Randal C.</creatorcontrib><creatorcontrib>Alvarez, David A.</creatorcontrib><creatorcontrib>Gala, William R.</creatorcontrib><creatorcontrib>Steen, Alexis</creatorcontrib><creatorcontrib>Gale, Robert</creatorcontrib><creatorcontrib>Ingersoll, Christopher G.</creatorcontrib><collection>Istex</collection><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>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>Environmental toxicology and chemistry</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Huckins, James N.</au><au>Prest, Harry F.</au><au>Petty, Jimmie D.</au><au>Lebo, Jon A.</au><au>Hodgins, Maureen M.</au><au>Clark, Randal C.</au><au>Alvarez, David A.</au><au>Gala, William R.</au><au>Steen, Alexis</au><au>Gale, Robert</au><au>Ingersoll, Christopher G.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Overview and comparison of lipid-containing semipermeable membrane devices and oysters (Crassostrea gigas) for assessing organic chemical exposure</atitle><jtitle>Environmental toxicology and chemistry</jtitle><addtitle>Environmental Toxicology and Chemistry</addtitle><date>2004-07</date><risdate>2004</risdate><volume>23</volume><issue>7</issue><spage>1617</spage><epage>1628</epage><pages>1617-1628</pages><issn>0730-7268</issn><eissn>1552-8618</eissn><coden>ETOCDK</coden><abstract>We performed 20‐d, flow‐through exposures of lipid‐containing semipermeable membrane devices (SPMDs) and Pacific oysters (Crassostrea gigas) to three concentrations (nominally 10, 100, and 250 ng/L) of a diverse mixture of polycyclic aromatic hydrocarbons (PAHs). Exposure water was seawater free of particulates larger than 0.1 μm. The results of these controlled laboratory studies demonstrated that SPMDs and oysters concentrate the same chemicals but that the relative amounts accumulated are different. For oysters, the 20‐d mean (across treatments) concentration factors (CFs) of test compounds with log Kow ≤ 4.8 were much lower (4.0‐ to 20‐fold lower) than those of the same compounds in SPMDs. In contrast, the 20‐d CFs of PAHs with log Kow ≥ 5.6 in oysters from the low‐level treatment were higher than the corresponding CFs for SPMDs. The CFs of these compounds in oysters from the low‐level treatment ranged from approximately 3.0‐ to 13‐fold higher than those in oysters from the high‐level treatment. This physiologically mediated difference in oyster CFs appears to be linked to active feeding in the low‐level treatment and to apparent toxicity‐induced cessation of feeding (i.e., valve closure) in the high‐level treatment. Because CFs for these compounds in oysters were not independent of exposure concentrations, it follows that tissue levels were not proportional to exposure concentration. However, both sampling approaches have advantages and disadvantages, and the appropriateness of their use depends on the goals of a given study.</abstract><cop>Hoboken</cop><pub>Wiley Periodicals, Inc</pub><pmid>15230313</pmid><doi>10.1897/03-366</doi><tpages>12</tpages></addata></record> |
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subjects | Animal, plant and microbial ecology Animals Applied ecology Biological and medical sciences Crassostrea gigas Ecotoxicology, biological effects of pollution Environmental Exposure Environmental Monitoring - methods Equilibrium Feeding Behavior Fundamental and applied biological sciences. Psychology General aspects Hydrophobic organic chemicals Kinetics Lipids - chemistry Membranes, Artificial Organic Chemicals - analysis Ostreidae - metabolism Oysters Polycyclic Aromatic Hydrocarbons - analysis Semipermeable membrane devices Specimen Handling Water Pollutants, Chemical - toxicity |
title | Overview and comparison of lipid-containing semipermeable membrane devices and oysters (Crassostrea gigas) for assessing organic chemical exposure |
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