Characterization of AHR2 and CYP1A expression in Atlantic sturgeon and shortnose sturgeon treated with coplanar PCBs and TCDD

•Cloning and characterization of AHR2 in endangered Atlantic sturgeon and shortnose sturgeon.•Significant expression of AHR2 and CYP1A in TCDD and coplanar PCB treated early life-stages at environmentally relevant doses.•Significant correlation between AHR2 and CYP1A expression in both sturgeons for...

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Veröffentlicht in:Aquatic toxicology 2018-04, Vol.197, p.19-31
Hauptverfasser: Roy, Nirmal K., Candelmo, Allison, DellaTorre, Melissa, Chambers, R. Christopher, Nádas, Arthur, Wirgin, Isaac
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container_issue
container_start_page 19
container_title Aquatic toxicology
container_volume 197
creator Roy, Nirmal K.
Candelmo, Allison
DellaTorre, Melissa
Chambers, R. Christopher
Nádas, Arthur
Wirgin, Isaac
description •Cloning and characterization of AHR2 in endangered Atlantic sturgeon and shortnose sturgeon.•Significant expression of AHR2 and CYP1A in TCDD and coplanar PCB treated early life-stages at environmentally relevant doses.•Significant correlation between AHR2 and CYP1A expression in both sturgeons for all chemicals.•Development of TEFs for coplanar PCBs in shortnose sturgeon. Atlantic sturgeon and shortnose sturgeon co-occur in many estuaries along the Atlantic Coast of North America. Both species are protected under the U.S. Endangered Species Act and internationally on the IUCN Red list and by CITES. Early life-stages of both sturgeons may be exposed to persistent aromatic hydrocarbon contaminants such as PCBs and PCDD/Fs which are at high levels in the sediments of impacted spawning rivers. Our objective was to compare the PCBs and TCDD sensitivities of both species with those of other fishes and to determine if environmental concentrations of these contaminants approach those that induce toxicity to their young life-stages under controlled laboratory conditions. Because our previous studies suggested that young life-stages of North American sturgeons are among the more sensitive of fishes to coplanar PCB and TCDD-induced toxicities, we were interested in identifying the molecular bases of this vulnerability. It is known that activation of the aryl hydrocarbon receptor 2 (AHR2) in fishes mediates most toxicities to these contaminants and transcriptional activation of xenobiotic metabolizing enzymes such as cytochrome P4501A (CYP1A). Previous studies demonstrated that structural and functional variations in AHRs are the bases for differing sensitivities of several vertebrate taxa to aromatic hydrocarbons. Therefore, in this study we characterized AHR2 and its expression in both sturgeons as an initial step in understanding the mechanistic bases of their sensitivities to these contaminants. We also used CYP1A expression as an endpoint to develop Toxicity Equivalency Factors (TEFs) for these sturgeons. We found that critical amino acid residues in the ligand binding domain of AHR2 in both sturgeons were identical to those of the aromatic hydrocarbon-sensitive white sturgeon, and differed from the less sensitive lake sturgeon. AHR2 expression was induced by TCDD (up to 6-fold) and by three of four tested coplanar PCB congeners (3–5-fold) in Atlantic sturgeon, but less so in shortnose sturgeon. We found that expression of AHR2 and CYP1A mRNA significantly cova
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Christopher ; Nádas, Arthur ; Wirgin, Isaac</creator><creatorcontrib>Roy, Nirmal K. ; Candelmo, Allison ; DellaTorre, Melissa ; Chambers, R. Christopher ; Nádas, Arthur ; Wirgin, Isaac</creatorcontrib><description>•Cloning and characterization of AHR2 in endangered Atlantic sturgeon and shortnose sturgeon.•Significant expression of AHR2 and CYP1A in TCDD and coplanar PCB treated early life-stages at environmentally relevant doses.•Significant correlation between AHR2 and CYP1A expression in both sturgeons for all chemicals.•Development of TEFs for coplanar PCBs in shortnose sturgeon. Atlantic sturgeon and shortnose sturgeon co-occur in many estuaries along the Atlantic Coast of North America. Both species are protected under the U.S. Endangered Species Act and internationally on the IUCN Red list and by CITES. Early life-stages of both sturgeons may be exposed to persistent aromatic hydrocarbon contaminants such as PCBs and PCDD/Fs which are at high levels in the sediments of impacted spawning rivers. Our objective was to compare the PCBs and TCDD sensitivities of both species with those of other fishes and to determine if environmental concentrations of these contaminants approach those that induce toxicity to their young life-stages under controlled laboratory conditions. Because our previous studies suggested that young life-stages of North American sturgeons are among the more sensitive of fishes to coplanar PCB and TCDD-induced toxicities, we were interested in identifying the molecular bases of this vulnerability. It is known that activation of the aryl hydrocarbon receptor 2 (AHR2) in fishes mediates most toxicities to these contaminants and transcriptional activation of xenobiotic metabolizing enzymes such as cytochrome P4501A (CYP1A). Previous studies demonstrated that structural and functional variations in AHRs are the bases for differing sensitivities of several vertebrate taxa to aromatic hydrocarbons. Therefore, in this study we characterized AHR2 and its expression in both sturgeons as an initial step in understanding the mechanistic bases of their sensitivities to these contaminants. We also used CYP1A expression as an endpoint to develop Toxicity Equivalency Factors (TEFs) for these sturgeons. We found that critical amino acid residues in the ligand binding domain of AHR2 in both sturgeons were identical to those of the aromatic hydrocarbon-sensitive white sturgeon, and differed from the less sensitive lake sturgeon. AHR2 expression was induced by TCDD (up to 6-fold) and by three of four tested coplanar PCB congeners (3–5-fold) in Atlantic sturgeon, but less so in shortnose sturgeon. We found that expression of AHR2 and CYP1A mRNA significantly covaried after exposure to TCDD and PCB77, PCB81, PCB126, but not PCB169 in both sturgeons. We also determined TEFs for the four coplanar PCBs in shortnose sturgeon based on comparison of CYP1A mRNA expression across all doses. Surprisingly, the TEFs for all four coplanar PCBs in shortnose sturgeon were much higher (6.4–162 times) than previously adopted for fishes by the WHO.</description><identifier>ISSN: 0166-445X</identifier><identifier>EISSN: 1879-1514</identifier><identifier>DOI: 10.1016/j.aquatox.2018.01.017</identifier><identifier>PMID: 29427830</identifier><language>eng</language><publisher>Netherlands: Elsevier B.V</publisher><subject>Acipenser brevirostrum ; Acipenser fulvescens ; Acipenser oxyrinchus ; Acipenser transmontanus ; AHR2 ; Amino Acid Sequence ; amino acids ; Animals ; Aroclors - toxicity ; aromatic hydrocarbons ; coasts ; Convention on International Trade in Endangered Species ; CYP1A ; Cytochrome P-450 CYP1A1 - genetics ; Cytochrome P-450 CYP1A1 - metabolism ; Endangered Species Act of 1973 ; enzymes ; estuaries ; Fishes - genetics ; Fishes - growth &amp; development ; Fishes - metabolism ; Gene expression ; Gene Expression Regulation - drug effects ; ligands ; messenger RNA ; PCBs ; Phylogeny ; polychlorinated biphenyls ; Polychlorinated Biphenyls - toxicity ; Polychlorinated Dibenzodioxins - toxicity ; polychlorinated dibenzofurans ; Receptors, Aryl Hydrocarbon - chemistry ; Receptors, Aryl Hydrocarbon - genetics ; Receptors, Aryl Hydrocarbon - metabolism ; rivers ; RNA, Messenger - genetics ; RNA, Messenger - metabolism ; sediments ; spawning ; sturgeon ; tetrachlorodibenzo-p-dioxin ; Toxic equivalency factors ; toxicity ; transcriptional activation ; United States ; Water Pollutants, Chemical - toxicity ; World Health Organization ; xenobiotics</subject><ispartof>Aquatic toxicology, 2018-04, Vol.197, p.19-31</ispartof><rights>2018 Elsevier B.V.</rights><rights>Copyright © 2018 Elsevier B.V. All rights reserved.</rights><lds50>peer_reviewed</lds50><oa>free_for_read</oa><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c500t-1c31deb01e9f4bb240ff6f3927e38ed696f3ec950674b08d93ba00e71f60cac53</citedby><cites>FETCH-LOGICAL-c500t-1c31deb01e9f4bb240ff6f3927e38ed696f3ec950674b08d93ba00e71f60cac53</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktohtml>$$Uhttps://dx.doi.org/10.1016/j.aquatox.2018.01.017$$EHTML$$P50$$Gelsevier$$H</linktohtml><link.rule.ids>230,314,777,781,882,3537,27905,27906,45976</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/29427830$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Roy, Nirmal K.</creatorcontrib><creatorcontrib>Candelmo, Allison</creatorcontrib><creatorcontrib>DellaTorre, Melissa</creatorcontrib><creatorcontrib>Chambers, R. Christopher</creatorcontrib><creatorcontrib>Nádas, Arthur</creatorcontrib><creatorcontrib>Wirgin, Isaac</creatorcontrib><title>Characterization of AHR2 and CYP1A expression in Atlantic sturgeon and shortnose sturgeon treated with coplanar PCBs and TCDD</title><title>Aquatic toxicology</title><addtitle>Aquat Toxicol</addtitle><description>•Cloning and characterization of AHR2 in endangered Atlantic sturgeon and shortnose sturgeon.•Significant expression of AHR2 and CYP1A in TCDD and coplanar PCB treated early life-stages at environmentally relevant doses.•Significant correlation between AHR2 and CYP1A expression in both sturgeons for all chemicals.•Development of TEFs for coplanar PCBs in shortnose sturgeon. Atlantic sturgeon and shortnose sturgeon co-occur in many estuaries along the Atlantic Coast of North America. Both species are protected under the U.S. Endangered Species Act and internationally on the IUCN Red list and by CITES. Early life-stages of both sturgeons may be exposed to persistent aromatic hydrocarbon contaminants such as PCBs and PCDD/Fs which are at high levels in the sediments of impacted spawning rivers. Our objective was to compare the PCBs and TCDD sensitivities of both species with those of other fishes and to determine if environmental concentrations of these contaminants approach those that induce toxicity to their young life-stages under controlled laboratory conditions. Because our previous studies suggested that young life-stages of North American sturgeons are among the more sensitive of fishes to coplanar PCB and TCDD-induced toxicities, we were interested in identifying the molecular bases of this vulnerability. It is known that activation of the aryl hydrocarbon receptor 2 (AHR2) in fishes mediates most toxicities to these contaminants and transcriptional activation of xenobiotic metabolizing enzymes such as cytochrome P4501A (CYP1A). Previous studies demonstrated that structural and functional variations in AHRs are the bases for differing sensitivities of several vertebrate taxa to aromatic hydrocarbons. Therefore, in this study we characterized AHR2 and its expression in both sturgeons as an initial step in understanding the mechanistic bases of their sensitivities to these contaminants. We also used CYP1A expression as an endpoint to develop Toxicity Equivalency Factors (TEFs) for these sturgeons. We found that critical amino acid residues in the ligand binding domain of AHR2 in both sturgeons were identical to those of the aromatic hydrocarbon-sensitive white sturgeon, and differed from the less sensitive lake sturgeon. AHR2 expression was induced by TCDD (up to 6-fold) and by three of four tested coplanar PCB congeners (3–5-fold) in Atlantic sturgeon, but less so in shortnose sturgeon. We found that expression of AHR2 and CYP1A mRNA significantly covaried after exposure to TCDD and PCB77, PCB81, PCB126, but not PCB169 in both sturgeons. We also determined TEFs for the four coplanar PCBs in shortnose sturgeon based on comparison of CYP1A mRNA expression across all doses. Surprisingly, the TEFs for all four coplanar PCBs in shortnose sturgeon were much higher (6.4–162 times) than previously adopted for fishes by the WHO.</description><subject>Acipenser brevirostrum</subject><subject>Acipenser fulvescens</subject><subject>Acipenser oxyrinchus</subject><subject>Acipenser transmontanus</subject><subject>AHR2</subject><subject>Amino Acid Sequence</subject><subject>amino acids</subject><subject>Animals</subject><subject>Aroclors - toxicity</subject><subject>aromatic hydrocarbons</subject><subject>coasts</subject><subject>Convention on International Trade in Endangered Species</subject><subject>CYP1A</subject><subject>Cytochrome P-450 CYP1A1 - genetics</subject><subject>Cytochrome P-450 CYP1A1 - metabolism</subject><subject>Endangered Species Act of 1973</subject><subject>enzymes</subject><subject>estuaries</subject><subject>Fishes - genetics</subject><subject>Fishes - growth &amp; development</subject><subject>Fishes - metabolism</subject><subject>Gene expression</subject><subject>Gene Expression Regulation - drug effects</subject><subject>ligands</subject><subject>messenger RNA</subject><subject>PCBs</subject><subject>Phylogeny</subject><subject>polychlorinated biphenyls</subject><subject>Polychlorinated Biphenyls - toxicity</subject><subject>Polychlorinated Dibenzodioxins - toxicity</subject><subject>polychlorinated dibenzofurans</subject><subject>Receptors, Aryl Hydrocarbon - chemistry</subject><subject>Receptors, Aryl Hydrocarbon - genetics</subject><subject>Receptors, Aryl Hydrocarbon - metabolism</subject><subject>rivers</subject><subject>RNA, Messenger - genetics</subject><subject>RNA, Messenger - metabolism</subject><subject>sediments</subject><subject>spawning</subject><subject>sturgeon</subject><subject>tetrachlorodibenzo-p-dioxin</subject><subject>Toxic equivalency factors</subject><subject>toxicity</subject><subject>transcriptional activation</subject><subject>United States</subject><subject>Water Pollutants, Chemical - toxicity</subject><subject>World Health Organization</subject><subject>xenobiotics</subject><issn>0166-445X</issn><issn>1879-1514</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2018</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNqFkVFv0zAQxy0EYmXwEUB-5CXl7NhJ_AIqGTCkSUxoSPBkOc5lddXGne2MbRLfHZeWAU9YJ1m--_3vbP8Jec5gzoBVr1ZzczWZ5G_mHFgzB5ajfkBmrKlVwSQTD8ksc1UhhPx6RJ7EuIK8uFCPyRFXgtdNCTPyo12aYGzC4O5Mcn6kfqCL08-cmrGn7bdztqB4sw0Y467oRrpIazMmZ2lMU7jEnNyRcelDGn3EP-kU0CTs6XeXltT6bZaZQM_bt_GX4qI9OXlKHg1mHfHZYT8mX96_u2hPi7NPHz62i7PCSoBUMFuyHjtgqAbRdVzAMFRDqXiNZYN9pfIBrZJQ1aKDpldlZwCwZkMF1lhZHpPX-77bqdtgb3FMwaz1NriNCbfaG6f_rYxuqS_9tZaNlFCr3ODloUHwVxPGpDcuWlznN6GfouYgZMNLziGjco_a4GMMONyPYaB31umVPlind9ZpYDnqrHvx9x3vVb-9ysCbPYD5p64dBh2tw9Fi7wLapHvv_jPiJ-uar8Y</recordid><startdate>20180401</startdate><enddate>20180401</enddate><creator>Roy, Nirmal K.</creator><creator>Candelmo, Allison</creator><creator>DellaTorre, Melissa</creator><creator>Chambers, R. Christopher</creator><creator>Nádas, Arthur</creator><creator>Wirgin, Isaac</creator><general>Elsevier B.V</general><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>7S9</scope><scope>L.6</scope><scope>5PM</scope></search><sort><creationdate>20180401</creationdate><title>Characterization of AHR2 and CYP1A expression in Atlantic sturgeon and shortnose sturgeon treated with coplanar PCBs and TCDD</title><author>Roy, Nirmal K. ; Candelmo, Allison ; DellaTorre, Melissa ; Chambers, R. Christopher ; Nádas, Arthur ; Wirgin, Isaac</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c500t-1c31deb01e9f4bb240ff6f3927e38ed696f3ec950674b08d93ba00e71f60cac53</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2018</creationdate><topic>Acipenser brevirostrum</topic><topic>Acipenser fulvescens</topic><topic>Acipenser oxyrinchus</topic><topic>Acipenser transmontanus</topic><topic>AHR2</topic><topic>Amino Acid Sequence</topic><topic>amino acids</topic><topic>Animals</topic><topic>Aroclors - toxicity</topic><topic>aromatic hydrocarbons</topic><topic>coasts</topic><topic>Convention on International Trade in Endangered Species</topic><topic>CYP1A</topic><topic>Cytochrome P-450 CYP1A1 - genetics</topic><topic>Cytochrome P-450 CYP1A1 - metabolism</topic><topic>Endangered Species Act of 1973</topic><topic>enzymes</topic><topic>estuaries</topic><topic>Fishes - genetics</topic><topic>Fishes - growth &amp; development</topic><topic>Fishes - metabolism</topic><topic>Gene expression</topic><topic>Gene Expression Regulation - drug effects</topic><topic>ligands</topic><topic>messenger RNA</topic><topic>PCBs</topic><topic>Phylogeny</topic><topic>polychlorinated biphenyls</topic><topic>Polychlorinated Biphenyls - toxicity</topic><topic>Polychlorinated Dibenzodioxins - toxicity</topic><topic>polychlorinated dibenzofurans</topic><topic>Receptors, Aryl Hydrocarbon - chemistry</topic><topic>Receptors, Aryl Hydrocarbon - genetics</topic><topic>Receptors, Aryl Hydrocarbon - metabolism</topic><topic>rivers</topic><topic>RNA, Messenger - genetics</topic><topic>RNA, Messenger - metabolism</topic><topic>sediments</topic><topic>spawning</topic><topic>sturgeon</topic><topic>tetrachlorodibenzo-p-dioxin</topic><topic>Toxic equivalency factors</topic><topic>toxicity</topic><topic>transcriptional activation</topic><topic>United States</topic><topic>Water Pollutants, Chemical - toxicity</topic><topic>World Health Organization</topic><topic>xenobiotics</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Roy, Nirmal K.</creatorcontrib><creatorcontrib>Candelmo, Allison</creatorcontrib><creatorcontrib>DellaTorre, Melissa</creatorcontrib><creatorcontrib>Chambers, R. Christopher</creatorcontrib><creatorcontrib>Nádas, Arthur</creatorcontrib><creatorcontrib>Wirgin, Isaac</creatorcontrib><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>AGRICOLA</collection><collection>AGRICOLA - Academic</collection><collection>PubMed Central (Full Participant titles)</collection><jtitle>Aquatic toxicology</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Roy, Nirmal K.</au><au>Candelmo, Allison</au><au>DellaTorre, Melissa</au><au>Chambers, R. Christopher</au><au>Nádas, Arthur</au><au>Wirgin, Isaac</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Characterization of AHR2 and CYP1A expression in Atlantic sturgeon and shortnose sturgeon treated with coplanar PCBs and TCDD</atitle><jtitle>Aquatic toxicology</jtitle><addtitle>Aquat Toxicol</addtitle><date>2018-04-01</date><risdate>2018</risdate><volume>197</volume><spage>19</spage><epage>31</epage><pages>19-31</pages><issn>0166-445X</issn><eissn>1879-1514</eissn><abstract>•Cloning and characterization of AHR2 in endangered Atlantic sturgeon and shortnose sturgeon.•Significant expression of AHR2 and CYP1A in TCDD and coplanar PCB treated early life-stages at environmentally relevant doses.•Significant correlation between AHR2 and CYP1A expression in both sturgeons for all chemicals.•Development of TEFs for coplanar PCBs in shortnose sturgeon. Atlantic sturgeon and shortnose sturgeon co-occur in many estuaries along the Atlantic Coast of North America. Both species are protected under the U.S. Endangered Species Act and internationally on the IUCN Red list and by CITES. Early life-stages of both sturgeons may be exposed to persistent aromatic hydrocarbon contaminants such as PCBs and PCDD/Fs which are at high levels in the sediments of impacted spawning rivers. Our objective was to compare the PCBs and TCDD sensitivities of both species with those of other fishes and to determine if environmental concentrations of these contaminants approach those that induce toxicity to their young life-stages under controlled laboratory conditions. Because our previous studies suggested that young life-stages of North American sturgeons are among the more sensitive of fishes to coplanar PCB and TCDD-induced toxicities, we were interested in identifying the molecular bases of this vulnerability. It is known that activation of the aryl hydrocarbon receptor 2 (AHR2) in fishes mediates most toxicities to these contaminants and transcriptional activation of xenobiotic metabolizing enzymes such as cytochrome P4501A (CYP1A). Previous studies demonstrated that structural and functional variations in AHRs are the bases for differing sensitivities of several vertebrate taxa to aromatic hydrocarbons. Therefore, in this study we characterized AHR2 and its expression in both sturgeons as an initial step in understanding the mechanistic bases of their sensitivities to these contaminants. We also used CYP1A expression as an endpoint to develop Toxicity Equivalency Factors (TEFs) for these sturgeons. We found that critical amino acid residues in the ligand binding domain of AHR2 in both sturgeons were identical to those of the aromatic hydrocarbon-sensitive white sturgeon, and differed from the less sensitive lake sturgeon. AHR2 expression was induced by TCDD (up to 6-fold) and by three of four tested coplanar PCB congeners (3–5-fold) in Atlantic sturgeon, but less so in shortnose sturgeon. We found that expression of AHR2 and CYP1A mRNA significantly covaried after exposure to TCDD and PCB77, PCB81, PCB126, but not PCB169 in both sturgeons. We also determined TEFs for the four coplanar PCBs in shortnose sturgeon based on comparison of CYP1A mRNA expression across all doses. Surprisingly, the TEFs for all four coplanar PCBs in shortnose sturgeon were much higher (6.4–162 times) than previously adopted for fishes by the WHO.</abstract><cop>Netherlands</cop><pub>Elsevier B.V</pub><pmid>29427830</pmid><doi>10.1016/j.aquatox.2018.01.017</doi><tpages>13</tpages><oa>free_for_read</oa></addata></record>
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source MEDLINE; Elsevier ScienceDirect Journals
subjects Acipenser brevirostrum
Acipenser fulvescens
Acipenser oxyrinchus
Acipenser transmontanus
AHR2
Amino Acid Sequence
amino acids
Animals
Aroclors - toxicity
aromatic hydrocarbons
coasts
Convention on International Trade in Endangered Species
CYP1A
Cytochrome P-450 CYP1A1 - genetics
Cytochrome P-450 CYP1A1 - metabolism
Endangered Species Act of 1973
enzymes
estuaries
Fishes - genetics
Fishes - growth & development
Fishes - metabolism
Gene expression
Gene Expression Regulation - drug effects
ligands
messenger RNA
PCBs
Phylogeny
polychlorinated biphenyls
Polychlorinated Biphenyls - toxicity
Polychlorinated Dibenzodioxins - toxicity
polychlorinated dibenzofurans
Receptors, Aryl Hydrocarbon - chemistry
Receptors, Aryl Hydrocarbon - genetics
Receptors, Aryl Hydrocarbon - metabolism
rivers
RNA, Messenger - genetics
RNA, Messenger - metabolism
sediments
spawning
sturgeon
tetrachlorodibenzo-p-dioxin
Toxic equivalency factors
toxicity
transcriptional activation
United States
Water Pollutants, Chemical - toxicity
World Health Organization
xenobiotics
title Characterization of AHR2 and CYP1A expression in Atlantic sturgeon and shortnose sturgeon treated with coplanar PCBs and TCDD
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