Relative Potencies and Combination Effects of Steroidal Estrogens in Fish
The natural steroids estradiol-17β (E2) and estrone (E1) and the synthetic steroid ethynylestradiol-17α (EE2) have frequently been measured in waters receiving domestic effluents. All of these steroids bind to the estrogen receptor(s) and have been shown to elicit a range of estrogenic responses in...
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description | The natural steroids estradiol-17β (E2) and estrone (E1) and the synthetic steroid ethynylestradiol-17α (EE2) have frequently been measured in waters receiving domestic effluents. All of these steroids bind to the estrogen receptor(s) and have been shown to elicit a range of estrogenic responses in fish at environmentally relevant concentrations. At present, however, no relative potency estimates have been derived for either the individual steroidal estrogens or their mixtures in vivo. In this study the estrogenic activity of E2, E1, and EE2, and the combination effects of a mixture of E2 and EE2 (equi-potent fixed-ratio mixture), were assessed using vitellogenin induction in a 14-day in vivo juvenile rainbow trout screening assay. Median effective concentrations, relative to E2, for induction of vitellogenin were determined from the concentration−response curves and the relative estrogenic potencies of each of the test chemicals calculated. Median effective concentrations were between 19 and 26 ng L-1 for E2, 60 ng L-1 for E1, and between 0.95 and 1.8 ng L-1 for EE2, implying that EE2 was approximately 11 to 27 times more potent than E2, while E2 was 2.3 to 3.2 times more potent than E1. The median effective concentration, relative to E2, for the binary mixture of E2 and EE2 was 15 ng L-1 (comprising 14.4 ng L-1 E2 and 0.6 ng L-1 EE2). Using the model of concentration addition it was shown that this activity of the binary mixture could be predicted from the activity of the individual chemicals. The ability of each individual steroid to contribute to the overall effect of a mixture, even at individual no-effect concentrations, combined with the high estrogenic potency of the steroids, particularly the synthetic steroid EE2, emphasizes the need to consider the total estrogenic load of these chemicals in our waterways. |
doi_str_mv | 10.1021/es0201348 |
format | Article |
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All of these steroids bind to the estrogen receptor(s) and have been shown to elicit a range of estrogenic responses in fish at environmentally relevant concentrations. At present, however, no relative potency estimates have been derived for either the individual steroidal estrogens or their mixtures in vivo. In this study the estrogenic activity of E2, E1, and EE2, and the combination effects of a mixture of E2 and EE2 (equi-potent fixed-ratio mixture), were assessed using vitellogenin induction in a 14-day in vivo juvenile rainbow trout screening assay. Median effective concentrations, relative to E2, for induction of vitellogenin were determined from the concentration−response curves and the relative estrogenic potencies of each of the test chemicals calculated. Median effective concentrations were between 19 and 26 ng L-1 for E2, 60 ng L-1 for E1, and between 0.95 and 1.8 ng L-1 for EE2, implying that EE2 was approximately 11 to 27 times more potent than E2, while E2 was 2.3 to 3.2 times more potent than E1. The median effective concentration, relative to E2, for the binary mixture of E2 and EE2 was 15 ng L-1 (comprising 14.4 ng L-1 E2 and 0.6 ng L-1 EE2). Using the model of concentration addition it was shown that this activity of the binary mixture could be predicted from the activity of the individual chemicals. The ability of each individual steroid to contribute to the overall effect of a mixture, even at individual no-effect concentrations, combined with the high estrogenic potency of the steroids, particularly the synthetic steroid EE2, emphasizes the need to consider the total estrogenic load of these chemicals in our waterways.</description><identifier>ISSN: 0013-936X</identifier><identifier>EISSN: 1520-5851</identifier><identifier>DOI: 10.1021/es0201348</identifier><identifier>PMID: 12680667</identifier><identifier>CODEN: ESTHAG</identifier><language>eng</language><publisher>Washington, DC: American Chemical Society</publisher><subject>Agnatha. Pisces ; Animal, plant and microbial ecology ; Animals ; Applied ecology ; Biological and medical sciences ; Drug Interactions ; Ecotoxicology, biological effects of pollution ; Effects of pollution and side effects of pesticides on vertebrates ; Estradiol - pharmacology ; Estradiol Congeners - pharmacology ; estradiol-17b ; Estrogens ; Estrone - pharmacology ; Ethinyl Estradiol - pharmacology ; ethynylestradiol-17a ; Female ; Fish ; Fundamental and applied biological sciences. Psychology ; Oncorhynchus mykiss ; Oncorhynchus mykiss - physiology ; Receptors, Estrogen - drug effects ; Steroids ; Vitellogenins - biosynthesis ; Water Pollutants, Chemical - pharmacology</subject><ispartof>Environmental science & technology, 2003-03, Vol.37 (6), p.1142-1149</ispartof><rights>Copyright © 2003 American Chemical Society</rights><rights>2003 INIST-CNRS</rights><rights>Copyright American Chemical Society Mar 15, 2003</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-a534t-c37832a479106b6556ef633e0ffffae7c5644aacc50aa263d985b4f38e4dd5543</citedby><cites>FETCH-LOGICAL-a534t-c37832a479106b6556ef633e0ffffae7c5644aacc50aa263d985b4f38e4dd5543</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://pubs.acs.org/doi/pdf/10.1021/es0201348$$EPDF$$P50$$Gacs$$H</linktopdf><linktohtml>$$Uhttps://pubs.acs.org/doi/10.1021/es0201348$$EHTML$$P50$$Gacs$$H</linktohtml><link.rule.ids>314,776,780,2752,27053,27901,27902,56713,56763</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=14660850$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/12680667$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Thorpe, Karen L</creatorcontrib><creatorcontrib>Cummings, Rob I</creatorcontrib><creatorcontrib>Hutchinson, Thomas H</creatorcontrib><creatorcontrib>Scholze, Martin</creatorcontrib><creatorcontrib>Brighty, Geoff</creatorcontrib><creatorcontrib>Sumpter, John P</creatorcontrib><creatorcontrib>Tyler, Charles R</creatorcontrib><title>Relative Potencies and Combination Effects of Steroidal Estrogens in Fish</title><title>Environmental science & technology</title><addtitle>Environ. Sci. Technol</addtitle><description>The natural steroids estradiol-17β (E2) and estrone (E1) and the synthetic steroid ethynylestradiol-17α (EE2) have frequently been measured in waters receiving domestic effluents. All of these steroids bind to the estrogen receptor(s) and have been shown to elicit a range of estrogenic responses in fish at environmentally relevant concentrations. At present, however, no relative potency estimates have been derived for either the individual steroidal estrogens or their mixtures in vivo. In this study the estrogenic activity of E2, E1, and EE2, and the combination effects of a mixture of E2 and EE2 (equi-potent fixed-ratio mixture), were assessed using vitellogenin induction in a 14-day in vivo juvenile rainbow trout screening assay. Median effective concentrations, relative to E2, for induction of vitellogenin were determined from the concentration−response curves and the relative estrogenic potencies of each of the test chemicals calculated. Median effective concentrations were between 19 and 26 ng L-1 for E2, 60 ng L-1 for E1, and between 0.95 and 1.8 ng L-1 for EE2, implying that EE2 was approximately 11 to 27 times more potent than E2, while E2 was 2.3 to 3.2 times more potent than E1. The median effective concentration, relative to E2, for the binary mixture of E2 and EE2 was 15 ng L-1 (comprising 14.4 ng L-1 E2 and 0.6 ng L-1 EE2). Using the model of concentration addition it was shown that this activity of the binary mixture could be predicted from the activity of the individual chemicals. The ability of each individual steroid to contribute to the overall effect of a mixture, even at individual no-effect concentrations, combined with the high estrogenic potency of the steroids, particularly the synthetic steroid EE2, emphasizes the need to consider the total estrogenic load of these chemicals in our waterways.</description><subject>Agnatha. Pisces</subject><subject>Animal, plant and microbial ecology</subject><subject>Animals</subject><subject>Applied ecology</subject><subject>Biological and medical sciences</subject><subject>Drug Interactions</subject><subject>Ecotoxicology, biological effects of pollution</subject><subject>Effects of pollution and side effects of pesticides on vertebrates</subject><subject>Estradiol - pharmacology</subject><subject>Estradiol Congeners - pharmacology</subject><subject>estradiol-17b</subject><subject>Estrogens</subject><subject>Estrone - pharmacology</subject><subject>Ethinyl Estradiol - pharmacology</subject><subject>ethynylestradiol-17a</subject><subject>Female</subject><subject>Fish</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>Oncorhynchus mykiss</subject><subject>Oncorhynchus mykiss - physiology</subject><subject>Receptors, Estrogen - drug effects</subject><subject>Steroids</subject><subject>Vitellogenins - biosynthesis</subject><subject>Water Pollutants, Chemical - pharmacology</subject><issn>0013-936X</issn><issn>1520-5851</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2003</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNqF0V1rFDEUBuAgFru2XvgHJAgKXow9-ZzMZVm2tbRgsfXjLmQzJ5o6O6nJrOi_N8suXdALcxPIeXjJOYeQ5wzeMuDsBAtwYEKaR2TGFIdGGcUekxnUx6YT-ssheVrKHQBwAeYJOWRcG9C6nZGLDzi4Kf5Eep0mHH3EQt3Y03laLeNYK2mkixDQT4WmQG8mzCn2bqCLMuX0FcdC40jPYvl2TA6CGwo-291H5OPZ4nb-rrl6f34xP71qnBJyarxojeBOth0DvdRKaQxaCIRQj8PWKy2lc94rcI5r0XdGLWUQBmXfKyXFEXm9zb3P6ccay2RXsXgcBjdiWhfLNNOCd-r_UGrFjd4kvvwL3qV1HmsTts6rMtlu0Jst8jmVkjHY-xxXLv-2DOxmC_ZhC9W-2AWulyvs93I39gpe7YAr3g0huzr5sndSazAKqmu2LpYJfz3UXf5ua0qr7O31je0-y0_68nxuYZ_rfNk38e8H_wCkQKet</recordid><startdate>20030315</startdate><enddate>20030315</enddate><creator>Thorpe, Karen L</creator><creator>Cummings, Rob I</creator><creator>Hutchinson, Thomas H</creator><creator>Scholze, Martin</creator><creator>Brighty, Geoff</creator><creator>Sumpter, John P</creator><creator>Tyler, Charles R</creator><general>American Chemical Society</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>7QO</scope><scope>7ST</scope><scope>7T7</scope><scope>7U7</scope><scope>8FD</scope><scope>C1K</scope><scope>FR3</scope><scope>P64</scope><scope>SOI</scope><scope>7QH</scope><scope>7TV</scope><scope>7UA</scope><scope>F1W</scope><scope>H97</scope><scope>L.G</scope></search><sort><creationdate>20030315</creationdate><title>Relative Potencies and Combination Effects of Steroidal Estrogens in Fish</title><author>Thorpe, Karen L ; Cummings, Rob I ; Hutchinson, Thomas H ; Scholze, Martin ; Brighty, Geoff ; Sumpter, John P ; Tyler, Charles R</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-a534t-c37832a479106b6556ef633e0ffffae7c5644aacc50aa263d985b4f38e4dd5543</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2003</creationdate><topic>Agnatha. Pisces</topic><topic>Animal, plant and microbial ecology</topic><topic>Animals</topic><topic>Applied ecology</topic><topic>Biological and medical sciences</topic><topic>Drug Interactions</topic><topic>Ecotoxicology, biological effects of pollution</topic><topic>Effects of pollution and side effects of pesticides on vertebrates</topic><topic>Estradiol - pharmacology</topic><topic>Estradiol Congeners - pharmacology</topic><topic>estradiol-17b</topic><topic>Estrogens</topic><topic>Estrone - pharmacology</topic><topic>Ethinyl Estradiol - pharmacology</topic><topic>ethynylestradiol-17a</topic><topic>Female</topic><topic>Fish</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>Oncorhynchus mykiss</topic><topic>Oncorhynchus mykiss - physiology</topic><topic>Receptors, Estrogen - drug effects</topic><topic>Steroids</topic><topic>Vitellogenins - biosynthesis</topic><topic>Water Pollutants, Chemical - pharmacology</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Thorpe, Karen L</creatorcontrib><creatorcontrib>Cummings, Rob I</creatorcontrib><creatorcontrib>Hutchinson, Thomas H</creatorcontrib><creatorcontrib>Scholze, Martin</creatorcontrib><creatorcontrib>Brighty, Geoff</creatorcontrib><creatorcontrib>Sumpter, John P</creatorcontrib><creatorcontrib>Tyler, Charles R</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>Biotechnology Research Abstracts</collection><collection>Environment Abstracts</collection><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Toxicology Abstracts</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Engineering Research Database</collection><collection>Biotechnology and BioEngineering Abstracts</collection><collection>Environment Abstracts</collection><collection>Aqualine</collection><collection>Pollution Abstracts</collection><collection>Water Resources Abstracts</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 3: Aquatic Pollution & Environmental Quality</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><jtitle>Environmental science & technology</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Thorpe, Karen L</au><au>Cummings, Rob I</au><au>Hutchinson, Thomas H</au><au>Scholze, Martin</au><au>Brighty, Geoff</au><au>Sumpter, John P</au><au>Tyler, Charles R</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Relative Potencies and Combination Effects of Steroidal Estrogens in Fish</atitle><jtitle>Environmental science & technology</jtitle><addtitle>Environ. Sci. Technol</addtitle><date>2003-03-15</date><risdate>2003</risdate><volume>37</volume><issue>6</issue><spage>1142</spage><epage>1149</epage><pages>1142-1149</pages><issn>0013-936X</issn><eissn>1520-5851</eissn><coden>ESTHAG</coden><abstract>The natural steroids estradiol-17β (E2) and estrone (E1) and the synthetic steroid ethynylestradiol-17α (EE2) have frequently been measured in waters receiving domestic effluents. All of these steroids bind to the estrogen receptor(s) and have been shown to elicit a range of estrogenic responses in fish at environmentally relevant concentrations. At present, however, no relative potency estimates have been derived for either the individual steroidal estrogens or their mixtures in vivo. In this study the estrogenic activity of E2, E1, and EE2, and the combination effects of a mixture of E2 and EE2 (equi-potent fixed-ratio mixture), were assessed using vitellogenin induction in a 14-day in vivo juvenile rainbow trout screening assay. Median effective concentrations, relative to E2, for induction of vitellogenin were determined from the concentration−response curves and the relative estrogenic potencies of each of the test chemicals calculated. Median effective concentrations were between 19 and 26 ng L-1 for E2, 60 ng L-1 for E1, and between 0.95 and 1.8 ng L-1 for EE2, implying that EE2 was approximately 11 to 27 times more potent than E2, while E2 was 2.3 to 3.2 times more potent than E1. The median effective concentration, relative to E2, for the binary mixture of E2 and EE2 was 15 ng L-1 (comprising 14.4 ng L-1 E2 and 0.6 ng L-1 EE2). Using the model of concentration addition it was shown that this activity of the binary mixture could be predicted from the activity of the individual chemicals. The ability of each individual steroid to contribute to the overall effect of a mixture, even at individual no-effect concentrations, combined with the high estrogenic potency of the steroids, particularly the synthetic steroid EE2, emphasizes the need to consider the total estrogenic load of these chemicals in our waterways.</abstract><cop>Washington, DC</cop><pub>American Chemical Society</pub><pmid>12680667</pmid><doi>10.1021/es0201348</doi><tpages>8</tpages></addata></record> |
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subjects | Agnatha. Pisces Animal, plant and microbial ecology Animals Applied ecology Biological and medical sciences Drug Interactions Ecotoxicology, biological effects of pollution Effects of pollution and side effects of pesticides on vertebrates Estradiol - pharmacology Estradiol Congeners - pharmacology estradiol-17b Estrogens Estrone - pharmacology Ethinyl Estradiol - pharmacology ethynylestradiol-17a Female Fish Fundamental and applied biological sciences. Psychology Oncorhynchus mykiss Oncorhynchus mykiss - physiology Receptors, Estrogen - drug effects Steroids Vitellogenins - biosynthesis Water Pollutants, Chemical - pharmacology |
title | Relative Potencies and Combination Effects of Steroidal Estrogens in Fish |
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