Concentrations of booster biocides in sediment and clams from Vietnam
An analytical method for the simultaneous determination of five booster biocides (Sea-Nine 211, Dichlofluanid, Duiron, Irgarol 1051 and Pyrithiones) and degradation product of Irgarol 1051 (M1) in sediment from Vietnam was developed by LC/MS-MS. The recovery rates and relative standard deviation of...
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| Veröffentlicht in: | Journal of the Marine Biological Association of the United Kingdom 2006-10, Vol.86 (5), p.1163-1170 |
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| creator | Harino, Hiroya Midorikawa, Sayaka Arai, Takaomi Ohji, Madoka Cu, Nguyen Duc Miyazaki, Nobuyuki |
| description | An analytical method for the simultaneous determination of five booster biocides (Sea-Nine 211, Dichlofluanid, Duiron, Irgarol 1051 and Pyrithiones) and degradation product of Irgarol 1051 (M1) in sediment from Vietnam was developed by LC/MS-MS. The recovery rates and relative standard deviation of the booster biocides in the sediment were in the range of 71–108% and 1.5–12%, respectively, and the detection limits were in the range of 0.04–2 μg kg−1 dry. An analytical method for the simultaneous determination of three booster biocides (Sea-Nine 211, Duiron and Irgarol 1051) and M1 in clams was also developed by LC/MS-MS. The recovery rates and relative standard deviations of the booster biocides in the biological samples were in the range of 60–99% and 3.4–6.8%, respectively, and the detection limits were in the range of 0.24–1.1 μg kg−1. The booster biocides in sediment from the coastal area of northern and central Vietnam were measured using this analytical method. Sea-Nine 211, Dichlofluanid, Duiron, Irgarol 1051, M1 and Pyrithiones were detected in the range of 0.09–1.3 μg kg−1 dry, |
| doi_str_mv | 10.1017/S0025315406014147 |
| format | Article |
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The recovery rates and relative standard deviation of the booster biocides in the sediment were in the range of 71–108% and 1.5–12%, respectively, and the detection limits were in the range of 0.04–2 μg kg−1 dry. An analytical method for the simultaneous determination of three booster biocides (Sea-Nine 211, Duiron and Irgarol 1051) and M1 in clams was also developed by LC/MS-MS. The recovery rates and relative standard deviations of the booster biocides in the biological samples were in the range of 60–99% and 3.4–6.8%, respectively, and the detection limits were in the range of 0.24–1.1 μg kg−1. The booster biocides in sediment from the coastal area of northern and central Vietnam were measured using this analytical method. Sea-Nine 211, Dichlofluanid, Duiron, Irgarol 1051, M1 and Pyrithiones were detected in the range of 0.09–1.3 μg kg−1 dry, <0.10–13 μg kg−1 dry, 0.11–3.0 μg kg−1 dry, 0.05–4.0 μg kg−1 dry, <0.1–0.43 μg kg−1 dry and <2–420 μg kg−1 dry, respectively. The detection frequencies of Dichlofluanid, M1 and Pyrithiones were low. The species and levels of detected booster biocides varied between sampling stations. Irgarol 1051 and its degradation product M1 were not detected in clams.</description><identifier>ISSN: 0025-3154</identifier><identifier>EISSN: 1469-7769</identifier><identifier>DOI: 10.1017/S0025315406014147</identifier><identifier>CODEN: JMBAAK</identifier><language>eng</language><publisher>Cambridge, UK: Cambridge University Press</publisher><subject>Analytical chemistry ; Analytical methods ; Animal and plant ecology ; Animal, plant and microbial ecology ; Biocides ; Biological and medical sciences ; Biological samples ; Coastal zone ; Coasts ; Detection limits ; Fundamental and applied biological sciences. Psychology ; Invertebrates ; Marine ; Meretrix ; Mollusca ; Mollusks ; Research Article ; Sea water ecosystems ; Sediments ; Standard deviation ; Synecology</subject><ispartof>Journal of the Marine Biological Association of the United Kingdom, 2006-10, Vol.86 (5), p.1163-1170</ispartof><rights>2006 Marine Biological Association of the United Kingdom</rights><rights>2006 INIST-CNRS</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c512t-377406c0c8ac8c83419107e9a261424678a41c8b38380d878a2c589fc8d059293</citedby></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktohtml>$$Uhttps://www.cambridge.org/core/product/identifier/S0025315406014147/type/journal_article$$EHTML$$P50$$Gcambridge$$H</linktohtml><link.rule.ids>164,314,780,784,27923,27924,55627</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=18135942$$DView record in Pascal Francis$$Hfree_for_read</backlink></links><search><creatorcontrib>Harino, Hiroya</creatorcontrib><creatorcontrib>Midorikawa, Sayaka</creatorcontrib><creatorcontrib>Arai, Takaomi</creatorcontrib><creatorcontrib>Ohji, Madoka</creatorcontrib><creatorcontrib>Cu, Nguyen Duc</creatorcontrib><creatorcontrib>Miyazaki, Nobuyuki</creatorcontrib><title>Concentrations of booster biocides in sediment and clams from Vietnam</title><title>Journal of the Marine Biological Association of the United Kingdom</title><addtitle>J. Mar. Biol. Ass</addtitle><description>An analytical method for the simultaneous determination of five booster biocides (Sea-Nine 211, Dichlofluanid, Duiron, Irgarol 1051 and Pyrithiones) and degradation product of Irgarol 1051 (M1) in sediment from Vietnam was developed by LC/MS-MS. The recovery rates and relative standard deviation of the booster biocides in the sediment were in the range of 71–108% and 1.5–12%, respectively, and the detection limits were in the range of 0.04–2 μg kg−1 dry. An analytical method for the simultaneous determination of three booster biocides (Sea-Nine 211, Duiron and Irgarol 1051) and M1 in clams was also developed by LC/MS-MS. The recovery rates and relative standard deviations of the booster biocides in the biological samples were in the range of 60–99% and 3.4–6.8%, respectively, and the detection limits were in the range of 0.24–1.1 μg kg−1. The booster biocides in sediment from the coastal area of northern and central Vietnam were measured using this analytical method. Sea-Nine 211, Dichlofluanid, Duiron, Irgarol 1051, M1 and Pyrithiones were detected in the range of 0.09–1.3 μg kg−1 dry, <0.10–13 μg kg−1 dry, 0.11–3.0 μg kg−1 dry, 0.05–4.0 μg kg−1 dry, <0.1–0.43 μg kg−1 dry and <2–420 μg kg−1 dry, respectively. The detection frequencies of Dichlofluanid, M1 and Pyrithiones were low. The species and levels of detected booster biocides varied between sampling stations. Irgarol 1051 and its degradation product M1 were not detected in clams.</description><subject>Analytical chemistry</subject><subject>Analytical methods</subject><subject>Animal and plant ecology</subject><subject>Animal, plant and microbial ecology</subject><subject>Biocides</subject><subject>Biological and medical sciences</subject><subject>Biological samples</subject><subject>Coastal zone</subject><subject>Coasts</subject><subject>Detection limits</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>Invertebrates</subject><subject>Marine</subject><subject>Meretrix</subject><subject>Mollusca</subject><subject>Mollusks</subject><subject>Research Article</subject><subject>Sea water ecosystems</subject><subject>Sediments</subject><subject>Standard deviation</subject><subject>Synecology</subject><issn>0025-3154</issn><issn>1469-7769</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2006</creationdate><recordtype>article</recordtype><sourceid>ABUWG</sourceid><sourceid>AFKRA</sourceid><sourceid>AZQEC</sourceid><sourceid>BENPR</sourceid><sourceid>CCPQU</sourceid><sourceid>DWQXO</sourceid><sourceid>GNUQQ</sourceid><recordid>eNqFkN1rFDEUxYNYcG37B_gWBH0bzc13HnXth7RUpK2ILyGbyUjqTFKTWWj_e7PsYqEifbpczu8ezj0IvQLyDgio95eEUMFAcCIJcODqGVoAl6ZTSprnaLGRu43-Ar2s9YYQAlLpBTpa5uRDmoubY04V5wGvcq5zKHgVs499qDgmXEMfp4Zhl3rsRzdVPJQ84W8xzMlNB2hvcGMNh7u5j66Pj66Wp935l5PPyw_nnRdA544p1fJ54rXz2mvGwQBRwTgqgVPeAjkOXq-YZpr0uq3UC20Gr3siDDVsH73d-t6W_Hsd6mynWH0YR5dCXldL25fCKHgSBMOASckb-PoReJPXJbUnLKUcBJFs4wZbyJdcawmDvS1xcuXeArGb-u0_9bebNztjV70bh-KSj_XhUAMThtPGdVsuttLv_uqu_LJSMSWsPPlqz74fX8gfH0_tp8azXRY3rUrsf4aHxP9P8weiwp_X</recordid><startdate>20061001</startdate><enddate>20061001</enddate><creator>Harino, Hiroya</creator><creator>Midorikawa, Sayaka</creator><creator>Arai, Takaomi</creator><creator>Ohji, Madoka</creator><creator>Cu, Nguyen Duc</creator><creator>Miyazaki, Nobuyuki</creator><general>Cambridge University Press</general><scope>BSCLL</scope><scope>IQODW</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>3V.</scope><scope>7QG</scope><scope>7SN</scope><scope>7TN</scope><scope>88A</scope><scope>8FE</scope><scope>8FH</scope><scope>8FK</scope><scope>ABUWG</scope><scope>AEUYN</scope><scope>AFKRA</scope><scope>AZQEC</scope><scope>BBNVY</scope><scope>BENPR</scope><scope>BHPHI</scope><scope>BKSAR</scope><scope>C1K</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>F1W</scope><scope>GNUQQ</scope><scope>H95</scope><scope>HCIFZ</scope><scope>L.G</scope><scope>LK8</scope><scope>M7N</scope><scope>M7P</scope><scope>PCBAR</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>7QH</scope><scope>H96</scope><scope>H97</scope></search><sort><creationdate>20061001</creationdate><title>Concentrations of booster biocides in sediment and clams from Vietnam</title><author>Harino, Hiroya ; Midorikawa, Sayaka ; Arai, Takaomi ; Ohji, Madoka ; Cu, Nguyen Duc ; Miyazaki, Nobuyuki</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c512t-377406c0c8ac8c83419107e9a261424678a41c8b38380d878a2c589fc8d059293</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2006</creationdate><topic>Analytical chemistry</topic><topic>Analytical methods</topic><topic>Animal and plant ecology</topic><topic>Animal, plant and microbial ecology</topic><topic>Biocides</topic><topic>Biological and medical sciences</topic><topic>Biological samples</topic><topic>Coastal zone</topic><topic>Coasts</topic><topic>Detection limits</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>Invertebrates</topic><topic>Marine</topic><topic>Meretrix</topic><topic>Mollusca</topic><topic>Mollusks</topic><topic>Research Article</topic><topic>Sea water ecosystems</topic><topic>Sediments</topic><topic>Standard deviation</topic><topic>Synecology</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Harino, Hiroya</creatorcontrib><creatorcontrib>Midorikawa, Sayaka</creatorcontrib><creatorcontrib>Arai, Takaomi</creatorcontrib><creatorcontrib>Ohji, Madoka</creatorcontrib><creatorcontrib>Cu, Nguyen Duc</creatorcontrib><creatorcontrib>Miyazaki, Nobuyuki</creatorcontrib><collection>Istex</collection><collection>Pascal-Francis</collection><collection>CrossRef</collection><collection>ProQuest Central (Corporate)</collection><collection>Animal Behavior Abstracts</collection><collection>Ecology Abstracts</collection><collection>Oceanic Abstracts</collection><collection>Biology Database (Alumni Edition)</collection><collection>ProQuest SciTech Collection</collection><collection>ProQuest Natural Science Collection</collection><collection>ProQuest Central (Alumni) (purchase pre-March 2016)</collection><collection>ProQuest Central (Alumni Edition)</collection><collection>ProQuest One Sustainability</collection><collection>ProQuest Central UK/Ireland</collection><collection>ProQuest Central Essentials</collection><collection>Biological Science Collection</collection><collection>ProQuest Central</collection><collection>Natural Science Collection</collection><collection>Earth, Atmospheric & Aquatic Science Collection</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ProQuest One Community College</collection><collection>ProQuest Central Korea</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>ProQuest Central Student</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 1: Biological Sciences & Living Resources</collection><collection>SciTech Premium Collection</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><collection>ProQuest Biological Science Collection</collection><collection>Algology Mycology and Protozoology Abstracts (Microbiology C)</collection><collection>Biological Science Database</collection><collection>Earth, Atmospheric & Aquatic Science Database</collection><collection>ProQuest One Academic Eastern Edition (DO NOT USE)</collection><collection>ProQuest One Academic</collection><collection>ProQuest One Academic UKI Edition</collection><collection>Aqualine</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 2: Ocean Technology, Policy & Non-Living Resources</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 3: Aquatic Pollution & Environmental Quality</collection><jtitle>Journal of the Marine Biological Association of the United Kingdom</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Harino, Hiroya</au><au>Midorikawa, Sayaka</au><au>Arai, Takaomi</au><au>Ohji, Madoka</au><au>Cu, Nguyen Duc</au><au>Miyazaki, Nobuyuki</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Concentrations of booster biocides in sediment and clams from Vietnam</atitle><jtitle>Journal of the Marine Biological Association of the United Kingdom</jtitle><addtitle>J. Mar. Biol. Ass</addtitle><date>2006-10-01</date><risdate>2006</risdate><volume>86</volume><issue>5</issue><spage>1163</spage><epage>1170</epage><pages>1163-1170</pages><issn>0025-3154</issn><eissn>1469-7769</eissn><coden>JMBAAK</coden><abstract>An analytical method for the simultaneous determination of five booster biocides (Sea-Nine 211, Dichlofluanid, Duiron, Irgarol 1051 and Pyrithiones) and degradation product of Irgarol 1051 (M1) in sediment from Vietnam was developed by LC/MS-MS. The recovery rates and relative standard deviation of the booster biocides in the sediment were in the range of 71–108% and 1.5–12%, respectively, and the detection limits were in the range of 0.04–2 μg kg−1 dry. An analytical method for the simultaneous determination of three booster biocides (Sea-Nine 211, Duiron and Irgarol 1051) and M1 in clams was also developed by LC/MS-MS. The recovery rates and relative standard deviations of the booster biocides in the biological samples were in the range of 60–99% and 3.4–6.8%, respectively, and the detection limits were in the range of 0.24–1.1 μg kg−1. The booster biocides in sediment from the coastal area of northern and central Vietnam were measured using this analytical method. Sea-Nine 211, Dichlofluanid, Duiron, Irgarol 1051, M1 and Pyrithiones were detected in the range of 0.09–1.3 μg kg−1 dry, <0.10–13 μg kg−1 dry, 0.11–3.0 μg kg−1 dry, 0.05–4.0 μg kg−1 dry, <0.1–0.43 μg kg−1 dry and <2–420 μg kg−1 dry, respectively. The detection frequencies of Dichlofluanid, M1 and Pyrithiones were low. The species and levels of detected booster biocides varied between sampling stations. Irgarol 1051 and its degradation product M1 were not detected in clams.</abstract><cop>Cambridge, UK</cop><pub>Cambridge University Press</pub><doi>10.1017/S0025315406014147</doi><tpages>8</tpages></addata></record> |
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| subjects | Analytical chemistry Analytical methods Animal and plant ecology Animal, plant and microbial ecology Biocides Biological and medical sciences Biological samples Coastal zone Coasts Detection limits Fundamental and applied biological sciences. Psychology Invertebrates Marine Meretrix Mollusca Mollusks Research Article Sea water ecosystems Sediments Standard deviation Synecology |
| title | Concentrations of booster biocides in sediment and clams from Vietnam |
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