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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Veröffentlicht in:Environmental science & technology 2003-03, Vol.37 (6), p.1142-1149
Hauptverfasser: Thorpe, Karen L, Cummings, Rob I, Hutchinson, Thomas H, Scholze, Martin, Brighty, Geoff, Sumpter, John P, Tyler, Charles R
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container_end_page 1149
container_issue 6
container_start_page 1142
container_title Environmental science & technology
container_volume 37
creator Thorpe, Karen L
Cummings, Rob I
Hutchinson, Thomas H
Scholze, Martin
Brighty, Geoff
Sumpter, John P
Tyler, Charles R
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
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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. 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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. 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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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