Mixture toxicity assessment of nickel and chlorpyrifos in the sea bass Dicentrarchus labrax.
Identifieur interne : 000043 ( Ncbi/Merge ); précédent : 000042; suivant : 000044Mixture toxicity assessment of nickel and chlorpyrifos in the sea bass Dicentrarchus labrax.
Auteurs : Mohamed Banni [Tunisie] ; Jamel Jebali ; Hamadi Guerbej ; Francesco Dondero ; Hamadi Boussetta ; Aldo ViarengoSource :
- Archives of environmental contamination and toxicology [ 1432-0703 ] ; 2011.
English descriptors
- KwdEn :
- Acetylcholinesterase (metabolism), Animals, Aquaculture, Bass (metabolism), Chlorpyrifos (analysis), Chlorpyrifos (metabolism), Chlorpyrifos (toxicity), Glutathione Transferase (metabolism), Liver (drug effects), Liver (enzymology), Liver (metabolism), Metallothionein (metabolism), NADPH-Ferrihemoprotein Reductase (metabolism), Nickel (analysis), Nickel (metabolism), Nickel (toxicity), Water Pollutants, Chemical (analysis), Water Pollutants, Chemical (metabolism), Water Pollutants, Chemical (toxicity).
- MESH :
- chemical , analysis : Chlorpyrifos, Nickel, Water Pollutants, Chemical.
- chemical , metabolism : Acetylcholinesterase, Chlorpyrifos, Glutathione Transferase, Metallothionein, NADPH-Ferrihemoprotein Reductase, Nickel, Water Pollutants, Chemical.
- drug effects : Liver.
- enzymology : Liver.
- metabolism : Bass, Liver.
- chemical , toxicity : Chlorpyrifos, Nickel, Water Pollutants, Chemical.
- Animals, Aquaculture.
Abstract
The present research work was designed to study Dicentrarchus labrax biotransformation and detoxification responses to acute exposure to nickel (Ni) and chlorpyrifos (CHP). Sexually immature sea bass were treated by intraperitoneal injection of nickel chloride (500 μg kg⁻¹), chlorpyrifos (10 mg kg⁻¹), and their binary mixture for 1, 3, and 7 days. Ni and CHP accumulation was quantified in liver after the exposure periods. The following biological responses were measured: (1) NADPH cytochrome P450 reductase (NCR) activity, as phase I biotransformation parameter; (2) gluthathione S-transferase (GST) activity as a phase II conjugation enzyme, acetylcholinesterase activity, and metallothionein (MT) content. Ni bioaccumulation in the liver resulted in an increasing uptake up to 15.48 μg g⁻¹ wet weight (Ni-treated animals) and 16.73 μg g⁻¹ wet weight (mixture-treated animals) after 7 days of exposure. CHP accumulation showed a distinct pattern in animals exposed to the mixture of chemicals in comparison with CHP-treated animals. NCR activity exhibited a marked activation in CHP and mixture-treated animals. GST activity was significantly increased starting from 1 day exposure in CHP-treated animals and after 3 days in Ni-treated animals. MT accumulation increased in all conditions, with a marked synergetic effect after 7 days of exposure. These data should be carefully considered in view of the biological effects of mixture pollutants, particularly in fish farming conditions.
DOI: 10.1007/s00244-010-9529-y
PubMed: 20422167
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Guerbej</name></author><author><name sortKey="Dondero, Francesco" sort="Dondero, Francesco" uniqKey="Dondero F" first="Francesco" last="Dondero">Francesco Dondero</name></author><author><name sortKey="Boussetta, Hamadi" sort="Boussetta, Hamadi" uniqKey="Boussetta H" first="Hamadi" last="Boussetta">Hamadi Boussetta</name></author><author><name sortKey="Viarengo, Aldo" sort="Viarengo, Aldo" uniqKey="Viarengo A" first="Aldo" last="Viarengo">Aldo Viarengo</name></author></analytic><series><title level="j">Archives of environmental contamination and toxicology</title><idno type="eISSN">1432-0703</idno><imprint><date when="2011" type="published">2011</date></imprint></series></biblStruct></sourceDesc></fileDesc><profileDesc><textClass><keywords scheme="KwdEn" xml:lang="en"><term>Acetylcholinesterase (metabolism)</term><term>Animals</term><term>Aquaculture</term><term>Bass (metabolism)</term><term>Chlorpyrifos (analysis)</term><term>Chlorpyrifos (metabolism)</term><term>Chlorpyrifos (toxicity)</term><term>Glutathione Transferase (metabolism)</term><term>Liver (drug effects)</term><term>Liver (enzymology)</term><term>Liver (metabolism)</term><term>Metallothionein (metabolism)</term><term>NADPH-Ferrihemoprotein Reductase (metabolism)</term><term>Nickel (analysis)</term><term>Nickel (metabolism)</term><term>Nickel (toxicity)</term><term>Water Pollutants, Chemical (analysis)</term><term>Water Pollutants, Chemical (metabolism)</term><term>Water Pollutants, Chemical (toxicity)</term></keywords><keywords scheme="MESH" type="chemical" qualifier="analysis" xml:lang="en"><term>Chlorpyrifos</term><term>Nickel</term><term>Water Pollutants, Chemical</term></keywords><keywords scheme="MESH" type="chemical" qualifier="metabolism" xml:lang="en"><term>Acetylcholinesterase</term><term>Chlorpyrifos</term><term>Glutathione Transferase</term><term>Metallothionein</term><term>NADPH-Ferrihemoprotein Reductase</term><term>Nickel</term><term>Water Pollutants, Chemical</term></keywords><keywords scheme="MESH" qualifier="drug effects" xml:lang="en"><term>Liver</term></keywords><keywords scheme="MESH" qualifier="enzymology" xml:lang="en"><term>Liver</term></keywords><keywords scheme="MESH" qualifier="metabolism" xml:lang="en"><term>Bass</term><term>Liver</term></keywords><keywords scheme="MESH" type="chemical" qualifier="toxicity" xml:lang="en"><term>Chlorpyrifos</term><term>Nickel</term><term>Water Pollutants, Chemical</term></keywords><keywords scheme="MESH" xml:lang="en"><term>Animals</term><term>Aquaculture</term></keywords></textClass></profileDesc></teiHeader><front><div type="abstract" xml:lang="en">The present research work was designed to study Dicentrarchus labrax biotransformation and detoxification responses to acute exposure to nickel (Ni) and chlorpyrifos (CHP). Sexually immature sea bass were treated by intraperitoneal injection of nickel chloride (500 μg kg⁻¹), chlorpyrifos (10 mg kg⁻¹), and their binary mixture for 1, 3, and 7 days. Ni and CHP accumulation was quantified in liver after the exposure periods. The following biological responses were measured: (1) NADPH cytochrome P450 reductase (NCR) activity, as phase I biotransformation parameter; (2) gluthathione S-transferase (GST) activity as a phase II conjugation enzyme, acetylcholinesterase activity, and metallothionein (MT) content. Ni bioaccumulation in the liver resulted in an increasing uptake up to 15.48 μg g⁻¹ wet weight (Ni-treated animals) and 16.73 μg g⁻¹ wet weight (mixture-treated animals) after 7 days of exposure. CHP accumulation showed a distinct pattern in animals exposed to the mixture of chemicals in comparison with CHP-treated animals. NCR activity exhibited a marked activation in CHP and mixture-treated animals. GST activity was significantly increased starting from 1 day exposure in CHP-treated animals and after 3 days in Ni-treated animals. MT accumulation increased in all conditions, with a marked synergetic effect after 7 days of exposure. These data should be carefully considered in view of the biological effects of mixture pollutants, particularly in fish farming conditions.</div></front></TEI><pubmed><MedlineCitation Status="MEDLINE" Owner="NLM"><PMID Version="1">20422167</PMID><DateCreated><Year>2011</Year><Month>01</Month><Day>12</Day></DateCreated><DateCompleted><Year>2011</Year><Month>04</Month><Day>20</Day></DateCompleted><DateRevised><Year>2015</Year><Month>11</Month><Day>19</Day></DateRevised><Article PubModel="Print-Electronic"><Journal><ISSN IssnType="Electronic">1432-0703</ISSN><JournalIssue CitedMedium="Internet"><Volume>60</Volume><Issue>1</Issue><PubDate><Year>2011</Year><Month>Jan</Month></PubDate></JournalIssue><Title>Archives of environmental contamination and toxicology</Title><ISOAbbreviation>Arch. Environ. Contam. Toxicol.</ISOAbbreviation></Journal><ArticleTitle>Mixture toxicity assessment of nickel and chlorpyrifos in the sea bass Dicentrarchus labrax.</ArticleTitle><Pagination><MedlinePgn>124-31</MedlinePgn></Pagination><ELocationID EIdType="doi" ValidYN="Y">10.1007/s00244-010-9529-y</ELocationID><Abstract><AbstractText>The present research work was designed to study Dicentrarchus labrax biotransformation and detoxification responses to acute exposure to nickel (Ni) and chlorpyrifos (CHP). Sexually immature sea bass were treated by intraperitoneal injection of nickel chloride (500 μg kg⁻¹), chlorpyrifos (10 mg kg⁻¹), and their binary mixture for 1, 3, and 7 days. Ni and CHP accumulation was quantified in liver after the exposure periods. The following biological responses were measured: (1) NADPH cytochrome P450 reductase (NCR) activity, as phase I biotransformation parameter; (2) gluthathione S-transferase (GST) activity as a phase II conjugation enzyme, acetylcholinesterase activity, and metallothionein (MT) content. Ni bioaccumulation in the liver resulted in an increasing uptake up to 15.48 μg g⁻¹ wet weight (Ni-treated animals) and 16.73 μg g⁻¹ wet weight (mixture-treated animals) after 7 days of exposure. CHP accumulation showed a distinct pattern in animals exposed to the mixture of chemicals in comparison with CHP-treated animals. NCR activity exhibited a marked activation in CHP and mixture-treated animals. GST activity was significantly increased starting from 1 day exposure in CHP-treated animals and after 3 days in Ni-treated animals. MT accumulation increased in all conditions, with a marked synergetic effect after 7 days of exposure. These data should be carefully considered in view of the biological effects of mixture pollutants, particularly in fish farming conditions.</AbstractText></Abstract><AuthorList CompleteYN="Y"><Author ValidYN="Y"><LastName>Banni</LastName><ForeName>Mohamed</ForeName><Initials>M</Initials><AffiliationInfo><Affiliation>Higher Institute of Agronomy, Chott-Mariem, Sousse, Tunisia. m_banni@yahoo.fr</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Jebali</LastName><ForeName>Jamel</ForeName><Initials>J</Initials></Author><Author ValidYN="Y"><LastName>Guerbej</LastName><ForeName>Hamadi</ForeName><Initials>H</Initials></Author><Author ValidYN="Y"><LastName>Dondero</LastName><ForeName>Francesco</ForeName><Initials>F</Initials></Author><Author ValidYN="Y"><LastName>Boussetta</LastName><ForeName>Hamadi</ForeName><Initials>H</Initials></Author><Author ValidYN="Y"><LastName>Viarengo</LastName><ForeName>Aldo</ForeName><Initials>A</Initials></Author></AuthorList><Language>eng</Language><PublicationTypeList><PublicationType UI="D016428">Journal Article</PublicationType><PublicationType UI="D013485">Research Support, Non-U.S. Gov't</PublicationType></PublicationTypeList><ArticleDate DateType="Electronic"><Year>2010</Year><Month>04</Month><Day>27</Day></ArticleDate></Article><MedlineJournalInfo><Country>United States</Country><MedlineTA>Arch Environ Contam Toxicol</MedlineTA><NlmUniqueID>0357245</NlmUniqueID><ISSNLinking>0090-4341</ISSNLinking></MedlineJournalInfo><ChemicalList><Chemical><RegistryNumber>0</RegistryNumber><NameOfSubstance UI="D014874">Water Pollutants, Chemical</NameOfSubstance></Chemical><Chemical><RegistryNumber>696BNE976J</RegistryNumber><NameOfSubstance UI="C022838">nickel chloride</NameOfSubstance></Chemical><Chemical><RegistryNumber>7OV03QG267</RegistryNumber><NameOfSubstance 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MajorTopicYN="N">enzymology</QualifierName><QualifierName UI="Q000378" MajorTopicYN="N">metabolism</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D008668" MajorTopicYN="N">Metallothionein</DescriptorName><QualifierName UI="Q000378" MajorTopicYN="N">metabolism</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D009251" MajorTopicYN="N">NADPH-Ferrihemoprotein Reductase</DescriptorName><QualifierName UI="Q000378" MajorTopicYN="N">metabolism</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D009532" MajorTopicYN="N">Nickel</DescriptorName><QualifierName UI="Q000032" MajorTopicYN="N">analysis</QualifierName><QualifierName UI="Q000378" MajorTopicYN="N">metabolism</QualifierName><QualifierName UI="Q000633" MajorTopicYN="Y">toxicity</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D014874" MajorTopicYN="N">Water Pollutants, Chemical</DescriptorName><QualifierName UI="Q000032" MajorTopicYN="N">analysis</QualifierName><QualifierName UI="Q000378" MajorTopicYN="N">metabolism</QualifierName><QualifierName UI="Q000633" MajorTopicYN="Y">toxicity</QualifierName></MeshHeading></MeshHeadingList></MedlineCitation><PubmedData><History><PubMedPubDate PubStatus="received"><Year>2010</Year><Month>02</Month><Day>12</Day></PubMedPubDate><PubMedPubDate PubStatus="accepted"><Year>2010</Year><Month>04</Month><Day>05</Day></PubMedPubDate><PubMedPubDate PubStatus="entrez"><Year>2010</Year><Month>4</Month><Day>28</Day><Hour>6</Hour><Minute>0</Minute></PubMedPubDate><PubMedPubDate PubStatus="pubmed"><Year>2010</Year><Month>4</Month><Day>28</Day><Hour>6</Hour><Minute>0</Minute></PubMedPubDate><PubMedPubDate PubStatus="medline"><Year>2011</Year><Month>4</Month><Day>22</Day><Hour>6</Hour><Minute>0</Minute></PubMedPubDate></History><PublicationStatus>ppublish</PublicationStatus><ArticleIdList><ArticleId IdType="pubmed">20422167</ArticleId><ArticleId IdType="doi">10.1007/s00244-010-9529-y</ArticleId></ArticleIdList></PubmedData></pubmed><affiliations><list><country><li>Tunisie</li></country></list><tree><noCountry><name sortKey="Boussetta, Hamadi" sort="Boussetta, Hamadi" uniqKey="Boussetta H" first="Hamadi" last="Boussetta">Hamadi Boussetta</name><name sortKey="Dondero, Francesco" sort="Dondero, Francesco" uniqKey="Dondero F" first="Francesco" last="Dondero">Francesco Dondero</name><name sortKey="Guerbej, Hamadi" sort="Guerbej, Hamadi" uniqKey="Guerbej H" first="Hamadi" last="Guerbej">Hamadi Guerbej</name><name sortKey="Jebali, Jamel" sort="Jebali, Jamel" uniqKey="Jebali J" first="Jamel" last="Jebali">Jamel Jebali</name><name sortKey="Viarengo, Aldo" sort="Viarengo, Aldo" uniqKey="Viarengo A" first="Aldo" last="Viarengo">Aldo Viarengo</name></noCountry><country name="Tunisie"><noRegion><name sortKey="Banni, Mohamed" sort="Banni, Mohamed" uniqKey="Banni M" first="Mohamed" last="Banni">Mohamed 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