Fuel oil and dispersant toxicity to the Antarctic sea urchin (Sterechinus neumayeri)
The risk of a major marine fuel spill in Antarctic waters is increasing, yet there are currently no standard or suitable response methods under extreme Antarctic conditions. Fuel dispersants may present a possible solution; however, little data exist on the toxicity of dispersants or fuels to Antarc...
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description | The risk of a major marine fuel spill in Antarctic waters is increasing, yet there are currently no standard or suitable response methods under extreme Antarctic conditions. Fuel dispersants may present a possible solution; however, little data exist on the toxicity of dispersants or fuels to Antarctic species, thereby preventing informed management decisions. Larval development toxicity tests using 3 life history stages of the Antarctic sea urchin (Sterechinus neumayeri) were completed to assess the toxicity of physically dispersed, chemically dispersed, and dispersant‐only water‐accommodated fractions (WAFs) of an intermediate fuel oil (IFO 180, BP) and the chemical dispersant Slickgone NS (Dasic International). Despite much lower total petroleum hydrocarbon concentrations, physically dispersed fuels contained higher proportions of low‐to‐intermediate weight carbon compounds and were generally at least an order of magnitude more toxic than chemically dispersed fuels. Based on concentrations that caused 50% abnormality (EC50) values, the embryonic unhatched blastula life stage was the least affected by fuels and dispersants, whereas the larval 4‐armed pluteus stage was the most sensitive. The present study is the first to investigate the possible implications of the use of fuel dispersants for fuel spill response in Antarctica. The results indicate that the use of a fuel dispersant did not increase the hydrocarbon toxicity of IFO 180 to the early life stages of Antarctic sea urchins, relative to physical dispersal. Environ Toxicol Chem 2017;36:1563–1571. © 2016 SETAC |
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Fuel dispersants may present a possible solution; however, little data exist on the toxicity of dispersants or fuels to Antarctic species, thereby preventing informed management decisions. Larval development toxicity tests using 3 life history stages of the Antarctic sea urchin (Sterechinus neumayeri) were completed to assess the toxicity of physically dispersed, chemically dispersed, and dispersant‐only water‐accommodated fractions (WAFs) of an intermediate fuel oil (IFO 180, BP) and the chemical dispersant Slickgone NS (Dasic International). Despite much lower total petroleum hydrocarbon concentrations, physically dispersed fuels contained higher proportions of low‐to‐intermediate weight carbon compounds and were generally at least an order of magnitude more toxic than chemically dispersed fuels. Based on concentrations that caused 50% abnormality (EC50) values, the embryonic unhatched blastula life stage was the least affected by fuels and dispersants, whereas the larval 4‐armed pluteus stage was the most sensitive. The present study is the first to investigate the possible implications of the use of fuel dispersants for fuel spill response in Antarctica. The results indicate that the use of a fuel dispersant did not increase the hydrocarbon toxicity of IFO 180 to the early life stages of Antarctic sea urchins, relative to physical dispersal. Environ Toxicol Chem 2017;36:1563–1571. © 2016 SETAC</description><identifier>ISSN: 0730-7268</identifier><identifier>EISSN: 1552-8618</identifier><identifier>DOI: 10.1002/etc.3679</identifier><identifier>PMID: 27813135</identifier><language>eng</language><publisher>United States: Blackwell Publishing Ltd</publisher><subject>Animals ; Antarctic ; Antarctic Regions ; Blastula ; Carbon compounds ; Developmental stages ; Dispersal ; Dispersant ; Dispersants ; Dispersion ; Embryos ; Fuel Oils - toxicity ; Fuels ; Hydrocarbons ; Hydrocarbons - chemistry ; Invertebrate toxicology ; Larval development ; Life history ; Marine biology ; Marine pollution ; Marine toxicity tests ; Oil spills ; Petroleum hydrocarbons ; Petroleum Pollution ; Pluteus ; Sea urchin ; Sea urchins ; Sea Urchins - drug effects ; Sea Urchins - growth & development ; Sterechinus neumayeri ; Toxicity ; Water Pollutants, Chemical - analysis ; Water Pollutants, Chemical - toxicity</subject><ispartof>Environmental toxicology and chemistry, 2017-06, Vol.36 (6), p.1563-1571</ispartof><rights>2016 SETAC</rights><rights>2016 SETAC.</rights><rights>2017 SETAC</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c4529-cd2857830aac0fae63c71acf5f3bbc94eb0f79debf2dbf797ee9b14224d0f3cc3</citedby><cites>FETCH-LOGICAL-c4529-cd2857830aac0fae63c71acf5f3bbc94eb0f79debf2dbf797ee9b14224d0f3cc3</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://onlinelibrary.wiley.com/doi/pdf/10.1002%2Fetc.3679$$EPDF$$P50$$Gwiley$$H</linktopdf><linktohtml>$$Uhttps://onlinelibrary.wiley.com/doi/full/10.1002%2Fetc.3679$$EHTML$$P50$$Gwiley$$H</linktohtml><link.rule.ids>314,780,784,1417,27924,27925,45574,45575</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/27813135$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Alexander, Frances J.</creatorcontrib><creatorcontrib>King, Catherine K.</creatorcontrib><creatorcontrib>Reichelt‐Brushett, Amanda J.</creatorcontrib><creatorcontrib>Harrison, Peter L.</creatorcontrib><title>Fuel oil and dispersant toxicity to the Antarctic sea urchin (Sterechinus neumayeri)</title><title>Environmental toxicology and chemistry</title><addtitle>Environ Toxicol Chem</addtitle><description>The risk of a major marine fuel spill in Antarctic waters is increasing, yet there are currently no standard or suitable response methods under extreme Antarctic conditions. Fuel dispersants may present a possible solution; however, little data exist on the toxicity of dispersants or fuels to Antarctic species, thereby preventing informed management decisions. Larval development toxicity tests using 3 life history stages of the Antarctic sea urchin (Sterechinus neumayeri) were completed to assess the toxicity of physically dispersed, chemically dispersed, and dispersant‐only water‐accommodated fractions (WAFs) of an intermediate fuel oil (IFO 180, BP) and the chemical dispersant Slickgone NS (Dasic International). Despite much lower total petroleum hydrocarbon concentrations, physically dispersed fuels contained higher proportions of low‐to‐intermediate weight carbon compounds and were generally at least an order of magnitude more toxic than chemically dispersed fuels. Based on concentrations that caused 50% abnormality (EC50) values, the embryonic unhatched blastula life stage was the least affected by fuels and dispersants, whereas the larval 4‐armed pluteus stage was the most sensitive. The present study is the first to investigate the possible implications of the use of fuel dispersants for fuel spill response in Antarctica. The results indicate that the use of a fuel dispersant did not increase the hydrocarbon toxicity of IFO 180 to the early life stages of Antarctic sea urchins, relative to physical dispersal. Environ Toxicol Chem 2017;36:1563–1571. © 2016 SETAC</description><subject>Animals</subject><subject>Antarctic</subject><subject>Antarctic Regions</subject><subject>Blastula</subject><subject>Carbon compounds</subject><subject>Developmental stages</subject><subject>Dispersal</subject><subject>Dispersant</subject><subject>Dispersants</subject><subject>Dispersion</subject><subject>Embryos</subject><subject>Fuel Oils - toxicity</subject><subject>Fuels</subject><subject>Hydrocarbons</subject><subject>Hydrocarbons - chemistry</subject><subject>Invertebrate toxicology</subject><subject>Larval development</subject><subject>Life history</subject><subject>Marine biology</subject><subject>Marine pollution</subject><subject>Marine toxicity tests</subject><subject>Oil spills</subject><subject>Petroleum hydrocarbons</subject><subject>Petroleum Pollution</subject><subject>Pluteus</subject><subject>Sea urchin</subject><subject>Sea urchins</subject><subject>Sea Urchins - drug effects</subject><subject>Sea Urchins - growth & development</subject><subject>Sterechinus neumayeri</subject><subject>Toxicity</subject><subject>Water Pollutants, Chemical - analysis</subject><subject>Water Pollutants, Chemical - toxicity</subject><issn>0730-7268</issn><issn>1552-8618</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2017</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNp1kE9LwzAYh4Mobk7BTyABL_PQmT9t0xzHcCoMPDjPIU3fsoyunUmK9tubOfXm6f0dHp4XHoSuKZlRQtg9BDPjuZAnaEyzjCVFTotTNCaCk0SwvBihC--3hNBcSnmORkwUlFOejdF62UODO9tg3Va4sn4Pzus24NB9WmPDEAcOG8DzNmhngjXYg8a9Mxvb4ulrAAeH2XvcQr_TAzh7d4nOat14uPq5E_S2fFgvnpLVy-PzYr5KTJoxmZiKFZkoONHakFpDzo2g2tRZzcvSyBRKUgtZQVmzqoxLAMiSpoylFam5MXyCbo_evevee_BBbbvetfGlopIwStMsJpig6ZEyrvPeQa32zu60GxQl6pBPxXzqkC-iNz_CvtxB9Qf-9opAcgQ-bAPDvyIVmW_hF18lehw</recordid><startdate>201706</startdate><enddate>201706</enddate><creator>Alexander, Frances J.</creator><creator>King, Catherine K.</creator><creator>Reichelt‐Brushett, Amanda J.</creator><creator>Harrison, Peter L.</creator><general>Blackwell Publishing Ltd</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>7QO</scope><scope>7SN</scope><scope>7SS</scope><scope>7ST</scope><scope>7T7</scope><scope>7TK</scope><scope>7U7</scope><scope>8FD</scope><scope>C1K</scope><scope>FR3</scope><scope>K9.</scope><scope>P64</scope><scope>RC3</scope><scope>SOI</scope></search><sort><creationdate>201706</creationdate><title>Fuel oil and dispersant toxicity to the Antarctic sea urchin (Sterechinus neumayeri)</title><author>Alexander, Frances J. ; King, Catherine K. ; Reichelt‐Brushett, Amanda J. ; Harrison, Peter L.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c4529-cd2857830aac0fae63c71acf5f3bbc94eb0f79debf2dbf797ee9b14224d0f3cc3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2017</creationdate><topic>Animals</topic><topic>Antarctic</topic><topic>Antarctic Regions</topic><topic>Blastula</topic><topic>Carbon compounds</topic><topic>Developmental stages</topic><topic>Dispersal</topic><topic>Dispersant</topic><topic>Dispersants</topic><topic>Dispersion</topic><topic>Embryos</topic><topic>Fuel Oils - toxicity</topic><topic>Fuels</topic><topic>Hydrocarbons</topic><topic>Hydrocarbons - chemistry</topic><topic>Invertebrate toxicology</topic><topic>Larval development</topic><topic>Life history</topic><topic>Marine biology</topic><topic>Marine pollution</topic><topic>Marine toxicity tests</topic><topic>Oil spills</topic><topic>Petroleum hydrocarbons</topic><topic>Petroleum Pollution</topic><topic>Pluteus</topic><topic>Sea urchin</topic><topic>Sea urchins</topic><topic>Sea Urchins - drug effects</topic><topic>Sea Urchins - growth & development</topic><topic>Sterechinus neumayeri</topic><topic>Toxicity</topic><topic>Water Pollutants, Chemical - analysis</topic><topic>Water Pollutants, Chemical - toxicity</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Alexander, Frances J.</creatorcontrib><creatorcontrib>King, Catherine K.</creatorcontrib><creatorcontrib>Reichelt‐Brushett, Amanda J.</creatorcontrib><creatorcontrib>Harrison, Peter L.</creatorcontrib><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>Ecology Abstracts</collection><collection>Entomology Abstracts (Full archive)</collection><collection>Environment Abstracts</collection><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Neurosciences Abstracts</collection><collection>Toxicology Abstracts</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Engineering Research Database</collection><collection>ProQuest Health & Medical Complete (Alumni)</collection><collection>Biotechnology and BioEngineering Abstracts</collection><collection>Genetics Abstracts</collection><collection>Environment Abstracts</collection><jtitle>Environmental toxicology and chemistry</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Alexander, Frances J.</au><au>King, Catherine K.</au><au>Reichelt‐Brushett, Amanda J.</au><au>Harrison, Peter L.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Fuel oil and dispersant toxicity to the Antarctic sea urchin (Sterechinus neumayeri)</atitle><jtitle>Environmental toxicology and chemistry</jtitle><addtitle>Environ Toxicol Chem</addtitle><date>2017-06</date><risdate>2017</risdate><volume>36</volume><issue>6</issue><spage>1563</spage><epage>1571</epage><pages>1563-1571</pages><issn>0730-7268</issn><eissn>1552-8618</eissn><abstract>The risk of a major marine fuel spill in Antarctic waters is increasing, yet there are currently no standard or suitable response methods under extreme Antarctic conditions. Fuel dispersants may present a possible solution; however, little data exist on the toxicity of dispersants or fuels to Antarctic species, thereby preventing informed management decisions. Larval development toxicity tests using 3 life history stages of the Antarctic sea urchin (Sterechinus neumayeri) were completed to assess the toxicity of physically dispersed, chemically dispersed, and dispersant‐only water‐accommodated fractions (WAFs) of an intermediate fuel oil (IFO 180, BP) and the chemical dispersant Slickgone NS (Dasic International). Despite much lower total petroleum hydrocarbon concentrations, physically dispersed fuels contained higher proportions of low‐to‐intermediate weight carbon compounds and were generally at least an order of magnitude more toxic than chemically dispersed fuels. Based on concentrations that caused 50% abnormality (EC50) values, the embryonic unhatched blastula life stage was the least affected by fuels and dispersants, whereas the larval 4‐armed pluteus stage was the most sensitive. The present study is the first to investigate the possible implications of the use of fuel dispersants for fuel spill response in Antarctica. The results indicate that the use of a fuel dispersant did not increase the hydrocarbon toxicity of IFO 180 to the early life stages of Antarctic sea urchins, relative to physical dispersal. Environ Toxicol Chem 2017;36:1563–1571. © 2016 SETAC</abstract><cop>United States</cop><pub>Blackwell Publishing Ltd</pub><pmid>27813135</pmid><doi>10.1002/etc.3679</doi><tpages>9</tpages></addata></record> |
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subjects | Animals Antarctic Antarctic Regions Blastula Carbon compounds Developmental stages Dispersal Dispersant Dispersants Dispersion Embryos Fuel Oils - toxicity Fuels Hydrocarbons Hydrocarbons - chemistry Invertebrate toxicology Larval development Life history Marine biology Marine pollution Marine toxicity tests Oil spills Petroleum hydrocarbons Petroleum Pollution Pluteus Sea urchin Sea urchins Sea Urchins - drug effects Sea Urchins - growth & development Sterechinus neumayeri Toxicity Water Pollutants, Chemical - analysis Water Pollutants, Chemical - toxicity |
title | Fuel oil and dispersant toxicity to the Antarctic sea urchin (Sterechinus neumayeri) |
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