Comparative effects of pH and Vision® herbicide on two life stages of four anuran amphibian species
Vision®, a glyphosate‐based herbicide containing a 15% (weight:weight) polyethoxylated tallow amine surfactant blend, and the concurrent factor of pH were tested to determine their interactive effects on early life‐stage anurans. Ninety‐six‐hour laboratory static renewal studies, using the embryonic...
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description | Vision®, a glyphosate‐based herbicide containing a 15% (weight:weight) polyethoxylated tallow amine surfactant blend, and the concurrent factor of pH were tested to determine their interactive effects on early life‐stage anurans. Ninety‐six‐hour laboratory static renewal studies, using the embryonic and larval life stages (Gosner 25) of Rana clamitans, R. pipiens, Bufo americanus, and Xenopus laevis, were performed under a central composite rotatable design. Mortality and the prevalence of malformations were modeled using generalized linear models with a profile deviance approach for obtaining confidence intervals. There was a significant (p < 0.05) interaction of pH with Vision concentration in all eight models, such that the toxicity of Vision was amplified by elevated pH. The surfactant is the major toxic component of Vision and is hypothesized, in this study, to be the source of the pH interaction. Larvae of B. americanus and R. clamitans were 1.5 to 3.8 times more sensitive than their corresponding embryos, whereas X. laevis and R. pipiens larvae were 6.8 to 8.9 times more sensitive. At pH values above 7.5, the Vision concentrations expected to kill 50% of the test larvae in 96‐h (96‐h lethal concentration [LC50]) were predicted to be below the expected environmental concentration (EEC) as calculated by Canadian regulatory authorities. The EEC value represents a worst‐case scenario for aerial Vision application and is calculated assuming an application of the maximum label rate (2.1 kg acid equivalents [a.e.]/ha) into a pond 15 cm in depth. The EEC of 1.4 mg a.e./L (4.5 mg/L Vision) was not exceeded by 96‐h LC50 values for the embryo test. The larvae of the four species were comparable in sensitivity. Field studies should be completed using the more sensitive larval life stage to test for Vision toxicity at actual environmental concentrations. |
doi_str_mv | 10.1897/03-115 |
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Ninety‐six‐hour laboratory static renewal studies, using the embryonic and larval life stages (Gosner 25) of Rana clamitans, R. pipiens, Bufo americanus, and Xenopus laevis, were performed under a central composite rotatable design. Mortality and the prevalence of malformations were modeled using generalized linear models with a profile deviance approach for obtaining confidence intervals. There was a significant (p < 0.05) interaction of pH with Vision concentration in all eight models, such that the toxicity of Vision was amplified by elevated pH. The surfactant is the major toxic component of Vision and is hypothesized, in this study, to be the source of the pH interaction. Larvae of B. americanus and R. clamitans were 1.5 to 3.8 times more sensitive than their corresponding embryos, whereas X. laevis and R. pipiens larvae were 6.8 to 8.9 times more sensitive. At pH values above 7.5, the Vision concentrations expected to kill 50% of the test larvae in 96‐h (96‐h lethal concentration [LC50]) were predicted to be below the expected environmental concentration (EEC) as calculated by Canadian regulatory authorities. The EEC value represents a worst‐case scenario for aerial Vision application and is calculated assuming an application of the maximum label rate (2.1 kg acid equivalents [a.e.]/ha) into a pond 15 cm in depth. The EEC of 1.4 mg a.e./L (4.5 mg/L Vision) was not exceeded by 96‐h LC50 values for the embryo test. The larvae of the four species were comparable in sensitivity. Field studies should be completed using the more sensitive larval life stage to test for Vision toxicity at actual environmental concentrations.</description><identifier>ISSN: 0730-7268</identifier><identifier>EISSN: 1552-8618</identifier><identifier>DOI: 10.1897/03-115</identifier><identifier>PMID: 15095875</identifier><identifier>CODEN: ETOCDK</identifier><language>eng</language><publisher>Hoboken: Wiley Periodicals, Inc</publisher><subject>Amhibians ; Animal, plant and microbial ecology ; Animals ; Applied ecology ; Aquatic toxicity ; Biological and medical sciences ; Bufo americanus ; Bufonidae - growth & development ; Congenital Abnormalities - veterinary ; Ecotoxicology, biological effects of pollution ; Effects of pollution and side effects of pesticides on vertebrates ; Freshwater ; Fundamental and applied biological sciences. Psychology ; Generalized linear models ; Glycine - analogs & derivatives ; Glycine - toxicity ; Glyphosate ; Herbicides - toxicity ; Hydrogen-Ion Concentration ; Larva - growth & development ; Lethal Dose 50 ; Life-stage sensitivity ; Models, Theoretical ; Rana ; Rana clamitans ; Rana pipiens ; Ranidae - growth & development ; Reptilia. Amphibia ; Vision ; Water Pollutants, Chemical - toxicity ; Xenopus laevis ; Xenopus laevis - growth & development</subject><ispartof>Environmental toxicology and chemistry, 2004-04, Vol.23 (4), p.815-822</ispartof><rights>Copyright © 2004 SETAC</rights><rights>2004 INIST-CNRS</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c4162-91a2348b6d3f3989e5e641dfdc46ecda17574fab18cee052047472aef5573c843</citedby><cites>FETCH-LOGICAL-c4162-91a2348b6d3f3989e5e641dfdc46ecda17574fab18cee052047472aef5573c843</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://onlinelibrary.wiley.com/doi/pdf/10.1897%2F03-115$$EPDF$$P50$$Gwiley$$H</linktopdf><linktohtml>$$Uhttps://onlinelibrary.wiley.com/doi/full/10.1897%2F03-115$$EHTML$$P50$$Gwiley$$H</linktohtml><link.rule.ids>309,310,314,780,784,789,790,1416,23928,23929,25138,27922,27923,45572,45573</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=15603986$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/15095875$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Edginton, Andrea N.</creatorcontrib><creatorcontrib>Sheridan, Patrick M.</creatorcontrib><creatorcontrib>Stephenson, Gerald R.</creatorcontrib><creatorcontrib>Thompson, Dean G.</creatorcontrib><creatorcontrib>Boermans, Herman J.</creatorcontrib><title>Comparative effects of pH and Vision® herbicide on two life stages of four anuran amphibian species</title><title>Environmental toxicology and chemistry</title><addtitle>Environmental Toxicology and Chemistry</addtitle><description>Vision®, a glyphosate‐based herbicide containing a 15% (weight:weight) polyethoxylated tallow amine surfactant blend, and the concurrent factor of pH were tested to determine their interactive effects on early life‐stage anurans. Ninety‐six‐hour laboratory static renewal studies, using the embryonic and larval life stages (Gosner 25) of Rana clamitans, R. pipiens, Bufo americanus, and Xenopus laevis, were performed under a central composite rotatable design. Mortality and the prevalence of malformations were modeled using generalized linear models with a profile deviance approach for obtaining confidence intervals. There was a significant (p < 0.05) interaction of pH with Vision concentration in all eight models, such that the toxicity of Vision was amplified by elevated pH. The surfactant is the major toxic component of Vision and is hypothesized, in this study, to be the source of the pH interaction. Larvae of B. americanus and R. clamitans were 1.5 to 3.8 times more sensitive than their corresponding embryos, whereas X. laevis and R. pipiens larvae were 6.8 to 8.9 times more sensitive. At pH values above 7.5, the Vision concentrations expected to kill 50% of the test larvae in 96‐h (96‐h lethal concentration [LC50]) were predicted to be below the expected environmental concentration (EEC) as calculated by Canadian regulatory authorities. The EEC value represents a worst‐case scenario for aerial Vision application and is calculated assuming an application of the maximum label rate (2.1 kg acid equivalents [a.e.]/ha) into a pond 15 cm in depth. The EEC of 1.4 mg a.e./L (4.5 mg/L Vision) was not exceeded by 96‐h LC50 values for the embryo test. The larvae of the four species were comparable in sensitivity. Field studies should be completed using the more sensitive larval life stage to test for Vision toxicity at actual environmental concentrations.</description><subject>Amhibians</subject><subject>Animal, plant and microbial ecology</subject><subject>Animals</subject><subject>Applied ecology</subject><subject>Aquatic toxicity</subject><subject>Biological and medical sciences</subject><subject>Bufo americanus</subject><subject>Bufonidae - growth & development</subject><subject>Congenital Abnormalities - veterinary</subject><subject>Ecotoxicology, biological effects of pollution</subject><subject>Effects of pollution and side effects of pesticides on vertebrates</subject><subject>Freshwater</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>Generalized linear models</subject><subject>Glycine - analogs & derivatives</subject><subject>Glycine - toxicity</subject><subject>Glyphosate</subject><subject>Herbicides - toxicity</subject><subject>Hydrogen-Ion Concentration</subject><subject>Larva - growth & development</subject><subject>Lethal Dose 50</subject><subject>Life-stage sensitivity</subject><subject>Models, Theoretical</subject><subject>Rana</subject><subject>Rana clamitans</subject><subject>Rana pipiens</subject><subject>Ranidae - growth & development</subject><subject>Reptilia. Amphibia</subject><subject>Vision</subject><subject>Water Pollutants, Chemical - toxicity</subject><subject>Xenopus laevis</subject><subject>Xenopus laevis - growth & development</subject><issn>0730-7268</issn><issn>1552-8618</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2004</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNp10M1u1DAUBWCrArXDUB4BeQO7gB3_ZgkDtIgRSKgFqRvLca5blyQOdkLpS_EQPBmGGVE2bGwvvnOtexB6RMkzqhv1nLCKUnGAVlSIutKS6ntoRRQjlaqlPkIPcr4mhMqmaQ7RERWkEVqJFeo2cZhssnP4Bhi8BzdnHD2eTrEdO_wp5BDHnz_wFaQ2uNABjiOebyLugwecZ3sJf7yPSyqJJdkR22G6Cm0orzyBC5Afovve9hmO9_canb95fbY5rbYfTt5uXmwrx6msq4bamnHdyo551ugGBEhOO985LsF1liqhuLct1Q6AiJpwxVVtwQuhmNOcrdHT3dwpxa8L5NkMITvoeztCXLKhpRZCmLqDLsWcE3gzpTDYdGsoMb_7NISZ0meBj_cTl3aA7o7tCyzgyR7Y7Gzvy_4u5H-cJGUVWRzduZvQw-1_vjNFCFmTmhFejjWqdpmQZ_j-N2PTFyMVU8J8fn9ixMuP7y5ebZnZsF90UZpm</recordid><startdate>200404</startdate><enddate>200404</enddate><creator>Edginton, Andrea N.</creator><creator>Sheridan, Patrick M.</creator><creator>Stephenson, Gerald R.</creator><creator>Thompson, Dean G.</creator><creator>Boermans, Herman J.</creator><general>Wiley Periodicals, Inc</general><general>SETAC</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>7QH</scope><scope>7TV</scope><scope>7U7</scope><scope>7UA</scope><scope>C1K</scope><scope>F1W</scope><scope>H97</scope><scope>L.G</scope></search><sort><creationdate>200404</creationdate><title>Comparative effects of pH and Vision® herbicide on two life stages of four anuran amphibian species</title><author>Edginton, Andrea N. ; Sheridan, Patrick M. ; Stephenson, Gerald R. ; Thompson, Dean G. ; Boermans, Herman J.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c4162-91a2348b6d3f3989e5e641dfdc46ecda17574fab18cee052047472aef5573c843</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2004</creationdate><topic>Amhibians</topic><topic>Animal, plant and microbial ecology</topic><topic>Animals</topic><topic>Applied ecology</topic><topic>Aquatic toxicity</topic><topic>Biological and medical sciences</topic><topic>Bufo americanus</topic><topic>Bufonidae - growth & development</topic><topic>Congenital Abnormalities - veterinary</topic><topic>Ecotoxicology, biological effects of pollution</topic><topic>Effects of pollution and side effects of pesticides on vertebrates</topic><topic>Freshwater</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>Generalized linear models</topic><topic>Glycine - analogs & derivatives</topic><topic>Glycine - toxicity</topic><topic>Glyphosate</topic><topic>Herbicides - toxicity</topic><topic>Hydrogen-Ion Concentration</topic><topic>Larva - growth & development</topic><topic>Lethal Dose 50</topic><topic>Life-stage sensitivity</topic><topic>Models, Theoretical</topic><topic>Rana</topic><topic>Rana clamitans</topic><topic>Rana pipiens</topic><topic>Ranidae - growth & development</topic><topic>Reptilia. Amphibia</topic><topic>Vision</topic><topic>Water Pollutants, Chemical - toxicity</topic><topic>Xenopus laevis</topic><topic>Xenopus laevis - growth & development</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Edginton, Andrea N.</creatorcontrib><creatorcontrib>Sheridan, Patrick M.</creatorcontrib><creatorcontrib>Stephenson, Gerald R.</creatorcontrib><creatorcontrib>Thompson, Dean G.</creatorcontrib><creatorcontrib>Boermans, Herman J.</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>Aqualine</collection><collection>Pollution Abstracts</collection><collection>Toxicology Abstracts</collection><collection>Water Resources Abstracts</collection><collection>Environmental Sciences and Pollution Management</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 toxicology and chemistry</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Edginton, Andrea N.</au><au>Sheridan, Patrick M.</au><au>Stephenson, Gerald R.</au><au>Thompson, Dean G.</au><au>Boermans, Herman J.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Comparative effects of pH and Vision® herbicide on two life stages of four anuran amphibian species</atitle><jtitle>Environmental toxicology and chemistry</jtitle><addtitle>Environmental Toxicology and Chemistry</addtitle><date>2004-04</date><risdate>2004</risdate><volume>23</volume><issue>4</issue><spage>815</spage><epage>822</epage><pages>815-822</pages><issn>0730-7268</issn><eissn>1552-8618</eissn><coden>ETOCDK</coden><abstract>Vision®, a glyphosate‐based herbicide containing a 15% (weight:weight) polyethoxylated tallow amine surfactant blend, and the concurrent factor of pH were tested to determine their interactive effects on early life‐stage anurans. Ninety‐six‐hour laboratory static renewal studies, using the embryonic and larval life stages (Gosner 25) of Rana clamitans, R. pipiens, Bufo americanus, and Xenopus laevis, were performed under a central composite rotatable design. Mortality and the prevalence of malformations were modeled using generalized linear models with a profile deviance approach for obtaining confidence intervals. There was a significant (p < 0.05) interaction of pH with Vision concentration in all eight models, such that the toxicity of Vision was amplified by elevated pH. The surfactant is the major toxic component of Vision and is hypothesized, in this study, to be the source of the pH interaction. Larvae of B. americanus and R. clamitans were 1.5 to 3.8 times more sensitive than their corresponding embryos, whereas X. laevis and R. pipiens larvae were 6.8 to 8.9 times more sensitive. At pH values above 7.5, the Vision concentrations expected to kill 50% of the test larvae in 96‐h (96‐h lethal concentration [LC50]) were predicted to be below the expected environmental concentration (EEC) as calculated by Canadian regulatory authorities. The EEC value represents a worst‐case scenario for aerial Vision application and is calculated assuming an application of the maximum label rate (2.1 kg acid equivalents [a.e.]/ha) into a pond 15 cm in depth. The EEC of 1.4 mg a.e./L (4.5 mg/L Vision) was not exceeded by 96‐h LC50 values for the embryo test. The larvae of the four species were comparable in sensitivity. Field studies should be completed using the more sensitive larval life stage to test for Vision toxicity at actual environmental concentrations.</abstract><cop>Hoboken</cop><pub>Wiley Periodicals, Inc</pub><pmid>15095875</pmid><doi>10.1897/03-115</doi><tpages>8</tpages></addata></record> |
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subjects | Amhibians Animal, plant and microbial ecology Animals Applied ecology Aquatic toxicity Biological and medical sciences Bufo americanus Bufonidae - growth & development Congenital Abnormalities - veterinary Ecotoxicology, biological effects of pollution Effects of pollution and side effects of pesticides on vertebrates Freshwater Fundamental and applied biological sciences. Psychology Generalized linear models Glycine - analogs & derivatives Glycine - toxicity Glyphosate Herbicides - toxicity Hydrogen-Ion Concentration Larva - growth & development Lethal Dose 50 Life-stage sensitivity Models, Theoretical Rana Rana clamitans Rana pipiens Ranidae - growth & development Reptilia. Amphibia Vision Water Pollutants, Chemical - toxicity Xenopus laevis Xenopus laevis - growth & development |
title | Comparative effects of pH and Vision® herbicide on two life stages of four anuran amphibian species |
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