An evaluation of 2,4-dichlorophenoxyacetic acid in the Amphibian Metamorphosis Assay and the Fish Short-Term Reproduction Assay

2,4-Dichlorophenoxyacetic acid (2,4-D) was evaluated in both the Amphibian Metamorphosis Assay (AMA) and the Fish Short Term Reproduction Assay (FSTRA). In the AMA, tadpoles were exposed to mean measured 2,4-D concentrations of 0 (water control), 0.273, 3.24, 38.0 and 113mg acid equivalents (ae)/L f...

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Veröffentlicht in:Ecotoxicology and environmental safety 2013-04, Vol.90, p.143-150
Hauptverfasser: Coady, Katherine, Marino, Troy, Thomas, Johnson, Sosinski, Lindsay, Neal, Barbara, Hammond, Larry
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Marino, Troy
Thomas, Johnson
Sosinski, Lindsay
Neal, Barbara
Hammond, Larry
description 2,4-Dichlorophenoxyacetic acid (2,4-D) was evaluated in both the Amphibian Metamorphosis Assay (AMA) and the Fish Short Term Reproduction Assay (FSTRA). In the AMA, tadpoles were exposed to mean measured 2,4-D concentrations of 0 (water control), 0.273, 3.24, 38.0 and 113mg acid equivalents (ae)/L for either seven or 21 days. In the FSTRA, fathead minnows were exposed to mean measured 2,4-D concentrations of 0 (water control), 0.245, 3.14, 34.0, and 96.5mg ae/L for 21 days. The respective concentrations of 2,4-D were not overtly toxic to either Xenopus laevis tadpoles or fathead minnows (Pimephales promelas). In the AMA, there were no signs of either advanced or delayed development, asynchronous development, or significant histopathological effects of the thyroid gland among 2,4-D exposed tadpoles evaluated on either day seven or day 21 of the exposure. Therefore, following the AMA decision logic, 2,4-D is considered “likely thyroid inactive” in the AMA with a No Observable Effect Concentration (NOEC) of 113mg ae 2,4-D/L. In the FSTRA, there were no significant differences between control and 2,4-D exposed fish in regard to fertility, wet weight, length, gonado-somatic indices, tubercle scores, or blood plasma concentrations of vitellogenin. Furthermore, there were no treatment-related histopathologic changes in the testes or ovaries in any 2,4-D exposed group. The only significant effect was a decrease in fecundity among fish exposed to 96.5mg ae 2,4-D/L. The cause of the reduced fecundity at the highest concentration of 2,4-D tested in the assay was most likely due to a generalized stress response in the fish, and not due to a specific endocrine mode of action of 2,4-D. Based on fish reproduction, the NOEC in the FSTRA was 34.0mg ae 2,4-D/L. ► 2,4-D showed no thyroid activity in the Amphibian Metamorphosis Assay. ► 2,4-D is likely not active in the androgen, estrogen, or HPG axis of fish. ► The NOEC for 2,4-D in the Amphibian Metamorphosis Assay was 113mg/L. ► The NOEC for 2,4-D based on fathead minnow reproduction was 34mg/L. ► The levels of 2,4-D in the environment do not pose a risk to aquatic organisms.
doi_str_mv 10.1016/j.ecoenv.2012.12.025
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In the AMA, tadpoles were exposed to mean measured 2,4-D concentrations of 0 (water control), 0.273, 3.24, 38.0 and 113mg acid equivalents (ae)/L for either seven or 21 days. In the FSTRA, fathead minnows were exposed to mean measured 2,4-D concentrations of 0 (water control), 0.245, 3.14, 34.0, and 96.5mg ae/L for 21 days. The respective concentrations of 2,4-D were not overtly toxic to either Xenopus laevis tadpoles or fathead minnows (Pimephales promelas). In the AMA, there were no signs of either advanced or delayed development, asynchronous development, or significant histopathological effects of the thyroid gland among 2,4-D exposed tadpoles evaluated on either day seven or day 21 of the exposure. Therefore, following the AMA decision logic, 2,4-D is considered “likely thyroid inactive” in the AMA with a No Observable Effect Concentration (NOEC) of 113mg ae 2,4-D/L. In the FSTRA, there were no significant differences between control and 2,4-D exposed fish in regard to fertility, wet weight, length, gonado-somatic indices, tubercle scores, or blood plasma concentrations of vitellogenin. Furthermore, there were no treatment-related histopathologic changes in the testes or ovaries in any 2,4-D exposed group. The only significant effect was a decrease in fecundity among fish exposed to 96.5mg ae 2,4-D/L. The cause of the reduced fecundity at the highest concentration of 2,4-D tested in the assay was most likely due to a generalized stress response in the fish, and not due to a specific endocrine mode of action of 2,4-D. 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Reptilia ; Amphibians ; Animal and plant ecology ; animal ovaries ; Animal, plant and microbial ecology ; Animals ; Applied ecology ; Assaying ; Biological and medical sciences ; Biological Assay ; blood plasma ; Cyprinidae - blood ; Cyprinidae - physiology ; Ecotoxicology, biological effects of pollution ; Endocrine ; Equivalence ; Exposure ; fecundity ; Female ; Fertility ; Fertility - drug effects ; Fish ; Fresh water ecosystems ; Freshwater ; Fundamental and applied biological sciences. Psychology ; General aspects ; histopathology ; Larva - drug effects ; Male ; mechanism of action ; metamorphosis ; minnows ; Ovary - chemistry ; Ovary - drug effects ; Pimephales promelas ; Reproduction ; Reproduction - drug effects ; Stress concentration ; stress response ; Synecology ; tadpoles ; Testes ; Testis - chemistry ; Testis - drug effects ; thyroid gland ; toxicity ; Vertebrates: general zoology, morphology, phylogeny, systematics, cytogenetics, geographical distribution ; vitellogenin ; Vitellogenins - analysis ; Vitellogenins - blood ; Water - chemistry ; Water Pollutants, Chemical - analysis ; Water Pollutants, Chemical - toxicity ; Xenopus laevis</subject><ispartof>Ecotoxicology and environmental safety, 2013-04, Vol.90, p.143-150</ispartof><rights>2013 Elsevier Inc.</rights><rights>2014 INIST-CNRS</rights><rights>Copyright © 2013 Elsevier Inc. 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In the AMA, tadpoles were exposed to mean measured 2,4-D concentrations of 0 (water control), 0.273, 3.24, 38.0 and 113mg acid equivalents (ae)/L for either seven or 21 days. In the FSTRA, fathead minnows were exposed to mean measured 2,4-D concentrations of 0 (water control), 0.245, 3.14, 34.0, and 96.5mg ae/L for 21 days. The respective concentrations of 2,4-D were not overtly toxic to either Xenopus laevis tadpoles or fathead minnows (Pimephales promelas). In the AMA, there were no signs of either advanced or delayed development, asynchronous development, or significant histopathological effects of the thyroid gland among 2,4-D exposed tadpoles evaluated on either day seven or day 21 of the exposure. Therefore, following the AMA decision logic, 2,4-D is considered “likely thyroid inactive” in the AMA with a No Observable Effect Concentration (NOEC) of 113mg ae 2,4-D/L. In the FSTRA, there were no significant differences between control and 2,4-D exposed fish in regard to fertility, wet weight, length, gonado-somatic indices, tubercle scores, or blood plasma concentrations of vitellogenin. Furthermore, there were no treatment-related histopathologic changes in the testes or ovaries in any 2,4-D exposed group. The only significant effect was a decrease in fecundity among fish exposed to 96.5mg ae 2,4-D/L. The cause of the reduced fecundity at the highest concentration of 2,4-D tested in the assay was most likely due to a generalized stress response in the fish, and not due to a specific endocrine mode of action of 2,4-D. Based on fish reproduction, the NOEC in the FSTRA was 34.0mg ae 2,4-D/L. ► 2,4-D showed no thyroid activity in the Amphibian Metamorphosis Assay. ► 2,4-D is likely not active in the androgen, estrogen, or HPG axis of fish. ► The NOEC for 2,4-D in the Amphibian Metamorphosis Assay was 113mg/L. ► The NOEC for 2,4-D based on fathead minnow reproduction was 34mg/L. ► The levels of 2,4-D in the environment do not pose a risk to aquatic organisms.</description><subject>2,4-D</subject><subject>2,4-Dichlorophenoxyacetic Acid - analysis</subject><subject>2,4-Dichlorophenoxyacetic Acid - toxicity</subject><subject>Amphibia. Reptilia</subject><subject>Amphibians</subject><subject>Animal and plant ecology</subject><subject>animal ovaries</subject><subject>Animal, plant and microbial ecology</subject><subject>Animals</subject><subject>Applied ecology</subject><subject>Assaying</subject><subject>Biological and medical sciences</subject><subject>Biological Assay</subject><subject>blood plasma</subject><subject>Cyprinidae - blood</subject><subject>Cyprinidae - physiology</subject><subject>Ecotoxicology, biological effects of pollution</subject><subject>Endocrine</subject><subject>Equivalence</subject><subject>Exposure</subject><subject>fecundity</subject><subject>Female</subject><subject>Fertility</subject><subject>Fertility - drug effects</subject><subject>Fish</subject><subject>Fresh water ecosystems</subject><subject>Freshwater</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>General aspects</subject><subject>histopathology</subject><subject>Larva - drug effects</subject><subject>Male</subject><subject>mechanism of action</subject><subject>metamorphosis</subject><subject>minnows</subject><subject>Ovary - chemistry</subject><subject>Ovary - drug effects</subject><subject>Pimephales promelas</subject><subject>Reproduction</subject><subject>Reproduction - drug effects</subject><subject>Stress concentration</subject><subject>stress response</subject><subject>Synecology</subject><subject>tadpoles</subject><subject>Testes</subject><subject>Testis - chemistry</subject><subject>Testis - drug effects</subject><subject>thyroid gland</subject><subject>toxicity</subject><subject>Vertebrates: general zoology, morphology, phylogeny, systematics, cytogenetics, geographical distribution</subject><subject>vitellogenin</subject><subject>Vitellogenins - analysis</subject><subject>Vitellogenins - blood</subject><subject>Water - chemistry</subject><subject>Water Pollutants, Chemical - analysis</subject><subject>Water Pollutants, Chemical - toxicity</subject><subject>Xenopus laevis</subject><issn>0147-6513</issn><issn>1090-2414</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2013</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNp9kU1v1DAQhiMEotvCP0DgCxIHsvgjjpNLpVVFAakIibZna9aeEK-SONjJij3x1-tuFrghjTSXZ-YdPZNlrxhdM8rKD7s1Go_Dfs0p4-tUlMsn2YrRmua8YMXTbEVZofJSMnGWnce4o5QKKuXz7IwLIZUsi1X2ezMQ3EM3w-T8QHxD-Psit860nQ9-bHHwvw5gcHKGgHGWuIFMLZJNP7Zu62AgX3GC3oex9dFFsokRDgQGe6SuXWzJbevDlN9h6Ml3HIO3szlmHdEX2bMGuogvT_0iu7_-eHf1Ob_59unL1eYmN0Utp7yinCGnpm5kBcKa0pRbtFVTmaTCKqGgEjWz0pTlllMAyiwwg4qmhkoqcZG9W_amA37OGCfdu2iw62BAP0fNBBdcsorVCS0W1AQfY8BGj8H1EA6aUf2oXu_0ol4_qtepkvo09vqUMG97tH-H_rhOwNsTANFA1wQYjIv_OMUp5SVP3JuFa8Br-BESc3-bkmT6H1VMiURcLgQmY3uHQUfjcDBoXUAzaevd_299AG9trdU</recordid><startdate>20130401</startdate><enddate>20130401</enddate><creator>Coady, Katherine</creator><creator>Marino, Troy</creator><creator>Thomas, Johnson</creator><creator>Sosinski, Lindsay</creator><creator>Neal, Barbara</creator><creator>Hammond, Larry</creator><general>Elsevier Inc</general><general>Elsevier</general><scope>6I.</scope><scope>AAFTH</scope><scope>FBQ</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>7SU</scope><scope>8FD</scope><scope>C1K</scope><scope>FR3</scope><scope>KR7</scope></search><sort><creationdate>20130401</creationdate><title>An evaluation of 2,4-dichlorophenoxyacetic acid in the Amphibian Metamorphosis Assay and the Fish Short-Term Reproduction Assay</title><author>Coady, Katherine ; Marino, Troy ; Thomas, Johnson ; Sosinski, Lindsay ; Neal, Barbara ; Hammond, Larry</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c495t-8021e20c9f58a3dc6c6bed8f8c016d737a8391d5c66b20aa01da1ce70da1e7573</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2013</creationdate><topic>2,4-D</topic><topic>2,4-Dichlorophenoxyacetic Acid - analysis</topic><topic>2,4-Dichlorophenoxyacetic Acid - toxicity</topic><topic>Amphibia. Reptilia</topic><topic>Amphibians</topic><topic>Animal and plant ecology</topic><topic>animal ovaries</topic><topic>Animal, plant and microbial ecology</topic><topic>Animals</topic><topic>Applied ecology</topic><topic>Assaying</topic><topic>Biological and medical sciences</topic><topic>Biological Assay</topic><topic>blood plasma</topic><topic>Cyprinidae - blood</topic><topic>Cyprinidae - physiology</topic><topic>Ecotoxicology, biological effects of pollution</topic><topic>Endocrine</topic><topic>Equivalence</topic><topic>Exposure</topic><topic>fecundity</topic><topic>Female</topic><topic>Fertility</topic><topic>Fertility - drug effects</topic><topic>Fish</topic><topic>Fresh water ecosystems</topic><topic>Freshwater</topic><topic>Fundamental and applied biological sciences. 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In the AMA, tadpoles were exposed to mean measured 2,4-D concentrations of 0 (water control), 0.273, 3.24, 38.0 and 113mg acid equivalents (ae)/L for either seven or 21 days. In the FSTRA, fathead minnows were exposed to mean measured 2,4-D concentrations of 0 (water control), 0.245, 3.14, 34.0, and 96.5mg ae/L for 21 days. The respective concentrations of 2,4-D were not overtly toxic to either Xenopus laevis tadpoles or fathead minnows (Pimephales promelas). In the AMA, there were no signs of either advanced or delayed development, asynchronous development, or significant histopathological effects of the thyroid gland among 2,4-D exposed tadpoles evaluated on either day seven or day 21 of the exposure. Therefore, following the AMA decision logic, 2,4-D is considered “likely thyroid inactive” in the AMA with a No Observable Effect Concentration (NOEC) of 113mg ae 2,4-D/L. In the FSTRA, there were no significant differences between control and 2,4-D exposed fish in regard to fertility, wet weight, length, gonado-somatic indices, tubercle scores, or blood plasma concentrations of vitellogenin. Furthermore, there were no treatment-related histopathologic changes in the testes or ovaries in any 2,4-D exposed group. The only significant effect was a decrease in fecundity among fish exposed to 96.5mg ae 2,4-D/L. The cause of the reduced fecundity at the highest concentration of 2,4-D tested in the assay was most likely due to a generalized stress response in the fish, and not due to a specific endocrine mode of action of 2,4-D. Based on fish reproduction, the NOEC in the FSTRA was 34.0mg ae 2,4-D/L. ► 2,4-D showed no thyroid activity in the Amphibian Metamorphosis Assay. ► 2,4-D is likely not active in the androgen, estrogen, or HPG axis of fish. ► The NOEC for 2,4-D in the Amphibian Metamorphosis Assay was 113mg/L. ► The NOEC for 2,4-D based on fathead minnow reproduction was 34mg/L. ► The levels of 2,4-D in the environment do not pose a risk to aquatic organisms.</abstract><cop>San Diego, CA</cop><pub>Elsevier Inc</pub><pmid>23357564</pmid><doi>10.1016/j.ecoenv.2012.12.025</doi><tpages>8</tpages><oa>free_for_read</oa></addata></record>
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subjects 2,4-D
2,4-Dichlorophenoxyacetic Acid - analysis
2,4-Dichlorophenoxyacetic Acid - toxicity
Amphibia. Reptilia
Amphibians
Animal and plant ecology
animal ovaries
Animal, plant and microbial ecology
Animals
Applied ecology
Assaying
Biological and medical sciences
Biological Assay
blood plasma
Cyprinidae - blood
Cyprinidae - physiology
Ecotoxicology, biological effects of pollution
Endocrine
Equivalence
Exposure
fecundity
Female
Fertility
Fertility - drug effects
Fish
Fresh water ecosystems
Freshwater
Fundamental and applied biological sciences. Psychology
General aspects
histopathology
Larva - drug effects
Male
mechanism of action
metamorphosis
minnows
Ovary - chemistry
Ovary - drug effects
Pimephales promelas
Reproduction
Reproduction - drug effects
Stress concentration
stress response
Synecology
tadpoles
Testes
Testis - chemistry
Testis - drug effects
thyroid gland
toxicity
Vertebrates: general zoology, morphology, phylogeny, systematics, cytogenetics, geographical distribution
vitellogenin
Vitellogenins - analysis
Vitellogenins - blood
Water - chemistry
Water Pollutants, Chemical - analysis
Water Pollutants, Chemical - toxicity
Xenopus laevis
title An evaluation of 2,4-dichlorophenoxyacetic acid in the Amphibian Metamorphosis Assay and the Fish Short-Term Reproduction Assay
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