Enhanced immunological and detoxification responses in Pacific oysters, Crassostrea gigas, exposed to chemically dispersed oil
The aim of this study was to evaluate the effects of chemically dispersed oil on an economically and ecologically important species inhabiting coasts and estuaries, the Pacific oyster Crassostrea gigas. Studies were carried out with juveniles, known to generally be more sensitive to environmental st...
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description | The aim of this study was to evaluate the effects of chemically dispersed oil on an economically and ecologically important species inhabiting coasts and estuaries, the Pacific oyster
Crassostrea gigas. Studies were carried out with juveniles, known to generally be more sensitive to environmental stress than adults. A set of enzyme activities involved in immune defence mechanisms and detoxification processes, i.e. superoxide dismutase (SOD), catalase, glutathione peroxidase (GPx), catecholase-type phenoloxidase (PO), laccase-type PO and lysozyme were analysed in different oyster tissues, i.e. the gills, digestive gland and mantle, and in the plasma and the haemoycte lysate supernatant (HLS) of the haemolymph. Results indicated that total PAH body burdens were 2.7 times higher in the presence than in the absence of the chemical dispersant. After 2 days of exposure to chemically dispersed oil, alkylated naphthalenes accounted for 55% of the total PAH body burden, whereas alkylated fluorenes and alkylated dibenzothiophenes accounted for 80% when the chemical dispersant was absent. Importantly, a higher number of enzyme activities were modified when oil was chemically dispersed, especially in the plasma and gills. Moreover, independently of the presence or absence of chemical dispersant, oil exposure generally inhibited enzyme activities in the gills and plasma, while they were generally activated in the mantle and haemocytes. These results suggest that the gills and plasma constitute sensitive compartments in
C. gigas, and that the mantle and haemocytes may play an important role in protection against xenobiotics. Among the six enzyme activities that were analysed in these body compartments, five were modulated in the chemical dispersion (CD) treatment while only half of the enzyme activities were modulated in the mechanical dispersion treatment. Furthermore, CD treatment effects were often observed following exposure, but also during depuration periods. These results suggest that immune and/or detoxification responses are likely to be affected when dispersants are used to treat oil spills in shallow waters.
► Total PAHs body burdens were 2.7 times higher with chemically dispersed oil than with mechanically dispersed oil. ► Significant correlations were observed between enzyme activities and PAH body burdens. ► The chemical dispersant alone modulated enzyme activities. ► Chemically dispersed oil enhanced modulation in immune and detoxification responses in
Cr |
doi_str_mv | 10.1016/j.watres.2011.05.011 |
format | Article |
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Crassostrea gigas. Studies were carried out with juveniles, known to generally be more sensitive to environmental stress than adults. A set of enzyme activities involved in immune defence mechanisms and detoxification processes, i.e. superoxide dismutase (SOD), catalase, glutathione peroxidase (GPx), catecholase-type phenoloxidase (PO), laccase-type PO and lysozyme were analysed in different oyster tissues, i.e. the gills, digestive gland and mantle, and in the plasma and the haemoycte lysate supernatant (HLS) of the haemolymph. Results indicated that total PAH body burdens were 2.7 times higher in the presence than in the absence of the chemical dispersant. After 2 days of exposure to chemically dispersed oil, alkylated naphthalenes accounted for 55% of the total PAH body burden, whereas alkylated fluorenes and alkylated dibenzothiophenes accounted for 80% when the chemical dispersant was absent. Importantly, a higher number of enzyme activities were modified when oil was chemically dispersed, especially in the plasma and gills. Moreover, independently of the presence or absence of chemical dispersant, oil exposure generally inhibited enzyme activities in the gills and plasma, while they were generally activated in the mantle and haemocytes. These results suggest that the gills and plasma constitute sensitive compartments in
C. gigas, and that the mantle and haemocytes may play an important role in protection against xenobiotics. Among the six enzyme activities that were analysed in these body compartments, five were modulated in the chemical dispersion (CD) treatment while only half of the enzyme activities were modulated in the mechanical dispersion treatment. Furthermore, CD treatment effects were often observed following exposure, but also during depuration periods. These results suggest that immune and/or detoxification responses are likely to be affected when dispersants are used to treat oil spills in shallow waters.
► Total PAHs body burdens were 2.7 times higher with chemically dispersed oil than with mechanically dispersed oil. ► Significant correlations were observed between enzyme activities and PAH body burdens. ► The chemical dispersant alone modulated enzyme activities. ► Chemically dispersed oil enhanced modulation in immune and detoxification responses in
Crassostrea gigas.</description><identifier>ISSN: 0043-1354</identifier><identifier>EISSN: 1879-2448</identifier><identifier>DOI: 10.1016/j.watres.2011.05.011</identifier><identifier>PMID: 21665240</identifier><identifier>CODEN: WATRAG</identifier><language>eng</language><publisher>Kidlington: Elsevier Ltd</publisher><subject>Alkylation ; Animals ; Applied sciences ; Bivalve ; Body Burden ; Chemical dispersion ; Crassostrea - chemistry ; Crassostrea - enzymology ; Crassostrea - immunology ; Crassostrea - metabolism ; Defence mechanisms ; Dispersants ; Dispersion ; Dispersions ; Ecotoxicology ; Environmental Monitoring ; Enzyme activity ; Exact sciences and technology ; Life Sciences ; Mantle ; Marine ; Muramidase - metabolism ; Oil spill ; Oxidoreductases - metabolism ; Oysters ; Petroleum - metabolism ; Petroleum - toxicity ; Pollution ; Polyallylamine hydrochloride ; Polycyclic Aromatic Hydrocarbons - immunology ; Polycyclic Aromatic Hydrocarbons - pharmacokinetics ; Polycyclic Aromatic Hydrocarbons - toxicity ; Principal Component Analysis ; Surface-Active Agents - metabolism ; Surface-Active Agents - toxicity ; Tissue-dependent response ; Toxicology ; Water Pollutants, Chemical - immunology ; Water Pollutants, Chemical - pharmacokinetics ; Water Pollutants, Chemical - toxicity ; Water treatment and pollution</subject><ispartof>Water research (Oxford), 2011-08, Vol.45 (14), p.4103-4118</ispartof><rights>2011 Elsevier Ltd</rights><rights>2015 INIST-CNRS</rights><rights>Copyright © 2011 Elsevier Ltd. All rights reserved.</rights><rights>Distributed under a Creative Commons Attribution 4.0 International License</rights><lds50>peer_reviewed</lds50><oa>free_for_read</oa><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c503t-a73a3960e2dcde84cfa79720428f6b9baf2546db2c2aa945c429db27135afa543</citedby><cites>FETCH-LOGICAL-c503t-a73a3960e2dcde84cfa79720428f6b9baf2546db2c2aa945c429db27135afa543</cites><orcidid>0000-0002-7932-6841 ; 0000-0002-5794-7284 ; 0000-0003-3877-9390 ; 0000-0003-0976-5600</orcidid></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktohtml>$$Uhttps://dx.doi.org/10.1016/j.watres.2011.05.011$$EHTML$$P50$$Gelsevier$$H</linktohtml><link.rule.ids>230,314,780,784,885,3550,27924,27925,45995</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=24314867$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/21665240$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink><backlink>$$Uhttps://hal.science/hal-00616692$$DView record in HAL$$Hfree_for_read</backlink></links><search><creatorcontrib>Luna-Acosta, A.</creatorcontrib><creatorcontrib>Kanan, R.</creatorcontrib><creatorcontrib>Le Floch, S.</creatorcontrib><creatorcontrib>Huet, V.</creatorcontrib><creatorcontrib>Pineau, P.</creatorcontrib><creatorcontrib>Bustamante, P.</creatorcontrib><creatorcontrib>Thomas-Guyon, H.</creatorcontrib><title>Enhanced immunological and detoxification responses in Pacific oysters, Crassostrea gigas, exposed to chemically dispersed oil</title><title>Water research (Oxford)</title><addtitle>Water Res</addtitle><description>The aim of this study was to evaluate the effects of chemically dispersed oil on an economically and ecologically important species inhabiting coasts and estuaries, the Pacific oyster
Crassostrea gigas. Studies were carried out with juveniles, known to generally be more sensitive to environmental stress than adults. A set of enzyme activities involved in immune defence mechanisms and detoxification processes, i.e. superoxide dismutase (SOD), catalase, glutathione peroxidase (GPx), catecholase-type phenoloxidase (PO), laccase-type PO and lysozyme were analysed in different oyster tissues, i.e. the gills, digestive gland and mantle, and in the plasma and the haemoycte lysate supernatant (HLS) of the haemolymph. Results indicated that total PAH body burdens were 2.7 times higher in the presence than in the absence of the chemical dispersant. After 2 days of exposure to chemically dispersed oil, alkylated naphthalenes accounted for 55% of the total PAH body burden, whereas alkylated fluorenes and alkylated dibenzothiophenes accounted for 80% when the chemical dispersant was absent. Importantly, a higher number of enzyme activities were modified when oil was chemically dispersed, especially in the plasma and gills. Moreover, independently of the presence or absence of chemical dispersant, oil exposure generally inhibited enzyme activities in the gills and plasma, while they were generally activated in the mantle and haemocytes. These results suggest that the gills and plasma constitute sensitive compartments in
C. gigas, and that the mantle and haemocytes may play an important role in protection against xenobiotics. Among the six enzyme activities that were analysed in these body compartments, five were modulated in the chemical dispersion (CD) treatment while only half of the enzyme activities were modulated in the mechanical dispersion treatment. Furthermore, CD treatment effects were often observed following exposure, but also during depuration periods. These results suggest that immune and/or detoxification responses are likely to be affected when dispersants are used to treat oil spills in shallow waters.
► Total PAHs body burdens were 2.7 times higher with chemically dispersed oil than with mechanically dispersed oil. ► Significant correlations were observed between enzyme activities and PAH body burdens. ► The chemical dispersant alone modulated enzyme activities. ► Chemically dispersed oil enhanced modulation in immune and detoxification responses in
Crassostrea gigas.</description><subject>Alkylation</subject><subject>Animals</subject><subject>Applied sciences</subject><subject>Bivalve</subject><subject>Body Burden</subject><subject>Chemical dispersion</subject><subject>Crassostrea - chemistry</subject><subject>Crassostrea - enzymology</subject><subject>Crassostrea - immunology</subject><subject>Crassostrea - metabolism</subject><subject>Defence mechanisms</subject><subject>Dispersants</subject><subject>Dispersion</subject><subject>Dispersions</subject><subject>Ecotoxicology</subject><subject>Environmental Monitoring</subject><subject>Enzyme activity</subject><subject>Exact sciences and technology</subject><subject>Life Sciences</subject><subject>Mantle</subject><subject>Marine</subject><subject>Muramidase - metabolism</subject><subject>Oil spill</subject><subject>Oxidoreductases - metabolism</subject><subject>Oysters</subject><subject>Petroleum - metabolism</subject><subject>Petroleum - toxicity</subject><subject>Pollution</subject><subject>Polyallylamine hydrochloride</subject><subject>Polycyclic Aromatic Hydrocarbons - immunology</subject><subject>Polycyclic Aromatic Hydrocarbons - pharmacokinetics</subject><subject>Polycyclic Aromatic Hydrocarbons - toxicity</subject><subject>Principal Component Analysis</subject><subject>Surface-Active Agents - metabolism</subject><subject>Surface-Active Agents - toxicity</subject><subject>Tissue-dependent response</subject><subject>Toxicology</subject><subject>Water Pollutants, Chemical - immunology</subject><subject>Water Pollutants, Chemical - pharmacokinetics</subject><subject>Water Pollutants, Chemical - toxicity</subject><subject>Water treatment and pollution</subject><issn>0043-1354</issn><issn>1879-2448</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2011</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNqFkU1v1DAQhi0EokvhHyDkC0JITbAdO4kvSNWqUKSV4ABna9Zxdr1K4uDJlu6lvx1HWcoNTq9m_MyH5yXkNWc5Z7z8cMh_wRQd5oJxnjOVJ3lCVryudCakrJ-SFWOyyHih5AV5gXhgjAlR6OfkQvCyVEKyFXm4GfYwWNdQ3_fHIXRh5y10FIaGNm4K975N8eTDQNOsMQzokPqBfgM7v9BwwslFvKLrCIgB00ZAd34HKeXux4Cp8xSo3bt-7tudaONxTBUpH3z3kjxroUP36qyX5Menm-_r22zz9fOX9fUms4oVUwZVAYUumRONbVwtbQuVrgSTom7Lrd5CK5Qsm62wAkBLZaXQKarS36EFJYtL8n7pu4fOjNH3EE8mgDe31xsz5xgr0020uOOJfbewYww_jw4n03u0rutgcOGIpq4LJnityv-Tlay1Ynom5ULaGBCjax-X4MzMdpqDWew0s52GKZMklb05Dzhue9c8Fv3xLwFvzwBgOm8bk5ce_3Ky4LIuq8R9XDiXjnznXTRovZt999HZyTTB_3uT30_UwU0</recordid><startdate>20110801</startdate><enddate>20110801</enddate><creator>Luna-Acosta, A.</creator><creator>Kanan, R.</creator><creator>Le Floch, S.</creator><creator>Huet, V.</creator><creator>Pineau, P.</creator><creator>Bustamante, P.</creator><creator>Thomas-Guyon, H.</creator><general>Elsevier Ltd</general><general>Elsevier</general><general>IWA Publishing/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>7X8</scope><scope>8FD</scope><scope>FR3</scope><scope>KR7</scope><scope>1XC</scope><scope>VOOES</scope><orcidid>https://orcid.org/0000-0002-7932-6841</orcidid><orcidid>https://orcid.org/0000-0002-5794-7284</orcidid><orcidid>https://orcid.org/0000-0003-3877-9390</orcidid><orcidid>https://orcid.org/0000-0003-0976-5600</orcidid></search><sort><creationdate>20110801</creationdate><title>Enhanced immunological and detoxification responses in Pacific oysters, Crassostrea gigas, exposed to chemically dispersed oil</title><author>Luna-Acosta, A. ; Kanan, R. ; Le Floch, S. ; Huet, V. ; Pineau, P. ; Bustamante, P. ; Thomas-Guyon, H.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c503t-a73a3960e2dcde84cfa79720428f6b9baf2546db2c2aa945c429db27135afa543</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2011</creationdate><topic>Alkylation</topic><topic>Animals</topic><topic>Applied sciences</topic><topic>Bivalve</topic><topic>Body Burden</topic><topic>Chemical dispersion</topic><topic>Crassostrea - chemistry</topic><topic>Crassostrea - enzymology</topic><topic>Crassostrea - immunology</topic><topic>Crassostrea - metabolism</topic><topic>Defence mechanisms</topic><topic>Dispersants</topic><topic>Dispersion</topic><topic>Dispersions</topic><topic>Ecotoxicology</topic><topic>Environmental Monitoring</topic><topic>Enzyme activity</topic><topic>Exact sciences and technology</topic><topic>Life Sciences</topic><topic>Mantle</topic><topic>Marine</topic><topic>Muramidase - metabolism</topic><topic>Oil spill</topic><topic>Oxidoreductases - metabolism</topic><topic>Oysters</topic><topic>Petroleum - metabolism</topic><topic>Petroleum - toxicity</topic><topic>Pollution</topic><topic>Polyallylamine hydrochloride</topic><topic>Polycyclic Aromatic Hydrocarbons - immunology</topic><topic>Polycyclic Aromatic Hydrocarbons - pharmacokinetics</topic><topic>Polycyclic Aromatic Hydrocarbons - toxicity</topic><topic>Principal Component Analysis</topic><topic>Surface-Active Agents - metabolism</topic><topic>Surface-Active Agents - toxicity</topic><topic>Tissue-dependent response</topic><topic>Toxicology</topic><topic>Water Pollutants, Chemical - immunology</topic><topic>Water Pollutants, Chemical - pharmacokinetics</topic><topic>Water Pollutants, Chemical - toxicity</topic><topic>Water treatment and pollution</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Luna-Acosta, A.</creatorcontrib><creatorcontrib>Kanan, R.</creatorcontrib><creatorcontrib>Le Floch, S.</creatorcontrib><creatorcontrib>Huet, V.</creatorcontrib><creatorcontrib>Pineau, P.</creatorcontrib><creatorcontrib>Bustamante, P.</creatorcontrib><creatorcontrib>Thomas-Guyon, H.</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>MEDLINE - Academic</collection><collection>Technology Research Database</collection><collection>Engineering Research Database</collection><collection>Civil Engineering Abstracts</collection><collection>Hyper Article en Ligne (HAL)</collection><collection>Hyper Article en Ligne (HAL) (Open Access)</collection><jtitle>Water research (Oxford)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Luna-Acosta, A.</au><au>Kanan, R.</au><au>Le Floch, S.</au><au>Huet, V.</au><au>Pineau, P.</au><au>Bustamante, P.</au><au>Thomas-Guyon, H.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Enhanced immunological and detoxification responses in Pacific oysters, Crassostrea gigas, exposed to chemically dispersed oil</atitle><jtitle>Water research (Oxford)</jtitle><addtitle>Water Res</addtitle><date>2011-08-01</date><risdate>2011</risdate><volume>45</volume><issue>14</issue><spage>4103</spage><epage>4118</epage><pages>4103-4118</pages><issn>0043-1354</issn><eissn>1879-2448</eissn><coden>WATRAG</coden><abstract>The aim of this study was to evaluate the effects of chemically dispersed oil on an economically and ecologically important species inhabiting coasts and estuaries, the Pacific oyster
Crassostrea gigas. Studies were carried out with juveniles, known to generally be more sensitive to environmental stress than adults. A set of enzyme activities involved in immune defence mechanisms and detoxification processes, i.e. superoxide dismutase (SOD), catalase, glutathione peroxidase (GPx), catecholase-type phenoloxidase (PO), laccase-type PO and lysozyme were analysed in different oyster tissues, i.e. the gills, digestive gland and mantle, and in the plasma and the haemoycte lysate supernatant (HLS) of the haemolymph. Results indicated that total PAH body burdens were 2.7 times higher in the presence than in the absence of the chemical dispersant. After 2 days of exposure to chemically dispersed oil, alkylated naphthalenes accounted for 55% of the total PAH body burden, whereas alkylated fluorenes and alkylated dibenzothiophenes accounted for 80% when the chemical dispersant was absent. Importantly, a higher number of enzyme activities were modified when oil was chemically dispersed, especially in the plasma and gills. Moreover, independently of the presence or absence of chemical dispersant, oil exposure generally inhibited enzyme activities in the gills and plasma, while they were generally activated in the mantle and haemocytes. These results suggest that the gills and plasma constitute sensitive compartments in
C. gigas, and that the mantle and haemocytes may play an important role in protection against xenobiotics. Among the six enzyme activities that were analysed in these body compartments, five were modulated in the chemical dispersion (CD) treatment while only half of the enzyme activities were modulated in the mechanical dispersion treatment. Furthermore, CD treatment effects were often observed following exposure, but also during depuration periods. These results suggest that immune and/or detoxification responses are likely to be affected when dispersants are used to treat oil spills in shallow waters.
► Total PAHs body burdens were 2.7 times higher with chemically dispersed oil than with mechanically dispersed oil. ► Significant correlations were observed between enzyme activities and PAH body burdens. ► The chemical dispersant alone modulated enzyme activities. ► Chemically dispersed oil enhanced modulation in immune and detoxification responses in
Crassostrea gigas.</abstract><cop>Kidlington</cop><pub>Elsevier Ltd</pub><pmid>21665240</pmid><doi>10.1016/j.watres.2011.05.011</doi><tpages>16</tpages><orcidid>https://orcid.org/0000-0002-7932-6841</orcidid><orcidid>https://orcid.org/0000-0002-5794-7284</orcidid><orcidid>https://orcid.org/0000-0003-3877-9390</orcidid><orcidid>https://orcid.org/0000-0003-0976-5600</orcidid><oa>free_for_read</oa></addata></record> |
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subjects | Alkylation Animals Applied sciences Bivalve Body Burden Chemical dispersion Crassostrea - chemistry Crassostrea - enzymology Crassostrea - immunology Crassostrea - metabolism Defence mechanisms Dispersants Dispersion Dispersions Ecotoxicology Environmental Monitoring Enzyme activity Exact sciences and technology Life Sciences Mantle Marine Muramidase - metabolism Oil spill Oxidoreductases - metabolism Oysters Petroleum - metabolism Petroleum - toxicity Pollution Polyallylamine hydrochloride Polycyclic Aromatic Hydrocarbons - immunology Polycyclic Aromatic Hydrocarbons - pharmacokinetics Polycyclic Aromatic Hydrocarbons - toxicity Principal Component Analysis Surface-Active Agents - metabolism Surface-Active Agents - toxicity Tissue-dependent response Toxicology Water Pollutants, Chemical - immunology Water Pollutants, Chemical - pharmacokinetics Water Pollutants, Chemical - toxicity Water treatment and pollution |
title | Enhanced immunological and detoxification responses in Pacific oysters, Crassostrea gigas, exposed to chemically dispersed oil |
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