Optimization of the polar organic chemical integrative sampler for the sampling of acidic and polar herbicides
This paper presents an optimization of the pharmaceutical Polar Organic Chemical Integrative Sampler (POCIS-200) under controlled laboratory conditions for the sampling of acidic (2,4-dichlorophenoxyacetic acid (2,4- D ), acetochlor ethanesulfonic acid (ESA), acetochlor oxanilic acid, bentazon, dica...
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description | This paper presents an optimization of the pharmaceutical Polar Organic Chemical Integrative Sampler (POCIS-200) under controlled laboratory conditions for the sampling of acidic (2,4-dichlorophenoxyacetic acid (2,4-
D
), acetochlor ethanesulfonic acid (ESA), acetochlor oxanilic acid, bentazon, dicamba, mesotrione, and metsulfuron) and polar (atrazine, diuron, and desisopropylatrazine) herbicides in water. Indeed, the conventional configuration of the POCIS-200 (46 cm
2
exposure window, 200 mg of Oasis® hydrophilic lipophilic balance (HLB) receiving phase) is not appropriate for the sampling of very polar and acidic compounds because they rapidly reach a thermodynamic equilibrium with the Oasis HLB receiving phase. Thus, we investigated several ways to extend the initial linear accumulation. On the one hand, increasing the mass of sorbent to 600 mg resulted in sampling rates (
R
s
s) twice as high as those observed with 200 mg (e.g., 287 vs. 157 mL day
−1
for acetochlor ESA). Although detection limits could thereby be reduced, most acidic analytes followed a biphasic uptake, proscribing the use of the conventional first-order model and preventing us from estimating time-weighted average concentrations. On the other hand, reducing the exposure window (3.1 vs. 46 cm
2
) allowed linear accumulations of all analytes over 35 days, but
R
s
s were dramatically reduced (e.g., 157 vs. 11 mL day
−1
for acetochlor ESA). Otherwise, the observation of biphasic releases of performance reference compounds (PRC), though mirroring acidic herbicide biphasic uptake, might complicate the implementation of the PRC approach to correct for environmental exposure conditions.
Figure
POCIS and μPOCIS in river media |
doi_str_mv | 10.1007/s00216-014-7757-0 |
format | Article |
fullrecord | <record><control><sourceid>gale_hal_p</sourceid><recordid>TN_cdi_hal_primary_oai_HAL_hal_02599817v1</recordid><sourceformat>XML</sourceformat><sourcesystem>PC</sourcesystem><galeid>A387652077</galeid><sourcerecordid>A387652077</sourcerecordid><originalsourceid>FETCH-LOGICAL-c618t-b6a556c38985649924dde3fdcc5f328d9784b8a5ed1ee1631484e7ed9bf247123</originalsourceid><addsrcrecordid>eNqNkk1v1DAQhiMEoqXwA7igSFzgkOJx_HlcVbRFWqkXOFteZ7LrKrEXO1up_HqcZlkhJATywfb4eWdG47eq3gK5BELkp0wIBdEQYI2UXDbkWXUOAlRDBSfPT2dGz6pXOd8TAlyBeFmdUSY0SArnVbjbT370P-zkY6hjX087rPdxsKmOaWuDd7Xb4eidHWofJtymQj5gne24HzDVfUxPkqe7D9s5hXW-KzobumOmHaaNL0HMr6sXvR0yvjnuF9W3689fr26b9d3Nl6vVunGl5anZCMu5cK3SigumNWVdh23fOcf7lqpOS8U2ynLsABFEC0wxlNjpTU-ZBNpeVB-XvDs7mH3yo02PJlpvbldrM8cI5VorkA9Q2A8Lu0_x-wHzZEafHQ6DDRgP2YAQhHAGXP8b5VwLKUvb_4GCoqwlkhf0_R_ofTykUOZTaktCheCaFOpyobZ2QONDH6dkXVnd_D0xYO9LfNUqKTglUhYBLAKXYs4J-9MggJjZP2bxjyn-MbN_zFzk3bGVw2bE7qT4ZZgC0AXI5SlsMf3W61-z_gQ0xs3h</addsrcrecordid><sourcetype>Open Access Repository</sourcetype><iscdi>true</iscdi><recordtype>article</recordtype><pqid>1670266590</pqid></control><display><type>article</type><title>Optimization of the polar organic chemical integrative sampler for the sampling of acidic and polar herbicides</title><source>SpringerLink Journals - AutoHoldings</source><creator>Fauvelle, Vincent ; Mazzella, Nicolas ; Belles, Angel ; Moreira, Aurélie ; Allan, Ian J. ; Budzinski, Hélène</creator><creatorcontrib>Fauvelle, Vincent ; Mazzella, Nicolas ; Belles, Angel ; Moreira, Aurélie ; Allan, Ian J. ; Budzinski, Hélène</creatorcontrib><description>This paper presents an optimization of the pharmaceutical Polar Organic Chemical Integrative Sampler (POCIS-200) under controlled laboratory conditions for the sampling of acidic (2,4-dichlorophenoxyacetic acid (2,4-
D
), acetochlor ethanesulfonic acid (ESA), acetochlor oxanilic acid, bentazon, dicamba, mesotrione, and metsulfuron) and polar (atrazine, diuron, and desisopropylatrazine) herbicides in water. Indeed, the conventional configuration of the POCIS-200 (46 cm
2
exposure window, 200 mg of Oasis® hydrophilic lipophilic balance (HLB) receiving phase) is not appropriate for the sampling of very polar and acidic compounds because they rapidly reach a thermodynamic equilibrium with the Oasis HLB receiving phase. Thus, we investigated several ways to extend the initial linear accumulation. On the one hand, increasing the mass of sorbent to 600 mg resulted in sampling rates (
R
s
s) twice as high as those observed with 200 mg (e.g., 287 vs. 157 mL day
−1
for acetochlor ESA). Although detection limits could thereby be reduced, most acidic analytes followed a biphasic uptake, proscribing the use of the conventional first-order model and preventing us from estimating time-weighted average concentrations. On the other hand, reducing the exposure window (3.1 vs. 46 cm
2
) allowed linear accumulations of all analytes over 35 days, but
R
s
s were dramatically reduced (e.g., 157 vs. 11 mL day
−1
for acetochlor ESA). Otherwise, the observation of biphasic releases of performance reference compounds (PRC), though mirroring acidic herbicide biphasic uptake, might complicate the implementation of the PRC approach to correct for environmental exposure conditions.
Figure
POCIS and μPOCIS in river media</description><identifier>ISSN: 1618-2642</identifier><identifier>EISSN: 1618-2650</identifier><identifier>DOI: 10.1007/s00216-014-7757-0</identifier><identifier>PMID: 24691721</identifier><language>eng</language><publisher>Berlin/Heidelberg: Springer Berlin Heidelberg</publisher><subject>Acetochlor ; Acids ; Analysis ; Analytical Chemistry ; Atrazine ; Biochemistry ; Characterization and Evaluation of Materials ; Chemistry ; Chemistry and Materials Science ; Contaminants ; Detection limits ; Dichlorophenoxyacetic acid ; Diuron ; Environmental conditions ; Environmental Sciences ; Equilibrium ; Food Science ; Herbicides ; Laboratory Medicine ; Metabolites ; Monitoring/Environmental Analysis ; Nucleic acids ; Optimization ; Organic chemicals ; Pesticides ; Pollutants ; Receiving ; Research Paper ; Samplers ; Sampling ; Thermodynamic equilibrium ; Thermodynamics ; Uptakes</subject><ispartof>Analytical and bioanalytical chemistry, 2014-05, Vol.406 (13), p.3191-3199</ispartof><rights>Springer-Verlag Berlin Heidelberg 2014</rights><rights>COPYRIGHT 2014 Springer</rights><rights>Distributed under a Creative Commons Attribution 4.0 International License</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c618t-b6a556c38985649924dde3fdcc5f328d9784b8a5ed1ee1631484e7ed9bf247123</citedby><cites>FETCH-LOGICAL-c618t-b6a556c38985649924dde3fdcc5f328d9784b8a5ed1ee1631484e7ed9bf247123</cites><orcidid>0000-0001-5282-9011 ; 0000-0003-1028-9154</orcidid></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://link.springer.com/content/pdf/10.1007/s00216-014-7757-0$$EPDF$$P50$$Gspringer$$H</linktopdf><linktohtml>$$Uhttps://link.springer.com/10.1007/s00216-014-7757-0$$EHTML$$P50$$Gspringer$$H</linktohtml><link.rule.ids>230,314,780,784,885,27923,27924,41487,42556,51318</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/24691721$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink><backlink>$$Uhttps://hal.inrae.fr/hal-02599817$$DView record in HAL$$Hfree_for_read</backlink></links><search><creatorcontrib>Fauvelle, Vincent</creatorcontrib><creatorcontrib>Mazzella, Nicolas</creatorcontrib><creatorcontrib>Belles, Angel</creatorcontrib><creatorcontrib>Moreira, Aurélie</creatorcontrib><creatorcontrib>Allan, Ian J.</creatorcontrib><creatorcontrib>Budzinski, Hélène</creatorcontrib><title>Optimization of the polar organic chemical integrative sampler for the sampling of acidic and polar herbicides</title><title>Analytical and bioanalytical chemistry</title><addtitle>Anal Bioanal Chem</addtitle><addtitle>Anal Bioanal Chem</addtitle><description>This paper presents an optimization of the pharmaceutical Polar Organic Chemical Integrative Sampler (POCIS-200) under controlled laboratory conditions for the sampling of acidic (2,4-dichlorophenoxyacetic acid (2,4-
D
), acetochlor ethanesulfonic acid (ESA), acetochlor oxanilic acid, bentazon, dicamba, mesotrione, and metsulfuron) and polar (atrazine, diuron, and desisopropylatrazine) herbicides in water. Indeed, the conventional configuration of the POCIS-200 (46 cm
2
exposure window, 200 mg of Oasis® hydrophilic lipophilic balance (HLB) receiving phase) is not appropriate for the sampling of very polar and acidic compounds because they rapidly reach a thermodynamic equilibrium with the Oasis HLB receiving phase. Thus, we investigated several ways to extend the initial linear accumulation. On the one hand, increasing the mass of sorbent to 600 mg resulted in sampling rates (
R
s
s) twice as high as those observed with 200 mg (e.g., 287 vs. 157 mL day
−1
for acetochlor ESA). Although detection limits could thereby be reduced, most acidic analytes followed a biphasic uptake, proscribing the use of the conventional first-order model and preventing us from estimating time-weighted average concentrations. On the other hand, reducing the exposure window (3.1 vs. 46 cm
2
) allowed linear accumulations of all analytes over 35 days, but
R
s
s were dramatically reduced (e.g., 157 vs. 11 mL day
−1
for acetochlor ESA). Otherwise, the observation of biphasic releases of performance reference compounds (PRC), though mirroring acidic herbicide biphasic uptake, might complicate the implementation of the PRC approach to correct for environmental exposure conditions.
Figure
POCIS and μPOCIS in river media</description><subject>Acetochlor</subject><subject>Acids</subject><subject>Analysis</subject><subject>Analytical Chemistry</subject><subject>Atrazine</subject><subject>Biochemistry</subject><subject>Characterization and Evaluation of Materials</subject><subject>Chemistry</subject><subject>Chemistry and Materials Science</subject><subject>Contaminants</subject><subject>Detection limits</subject><subject>Dichlorophenoxyacetic acid</subject><subject>Diuron</subject><subject>Environmental conditions</subject><subject>Environmental Sciences</subject><subject>Equilibrium</subject><subject>Food Science</subject><subject>Herbicides</subject><subject>Laboratory Medicine</subject><subject>Metabolites</subject><subject>Monitoring/Environmental Analysis</subject><subject>Nucleic acids</subject><subject>Optimization</subject><subject>Organic chemicals</subject><subject>Pesticides</subject><subject>Pollutants</subject><subject>Receiving</subject><subject>Research Paper</subject><subject>Samplers</subject><subject>Sampling</subject><subject>Thermodynamic 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of the polar organic chemical integrative sampler for the sampling of acidic and polar herbicides</title><author>Fauvelle, Vincent ; Mazzella, Nicolas ; Belles, Angel ; Moreira, Aurélie ; Allan, Ian J. ; Budzinski, Hélène</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c618t-b6a556c38985649924dde3fdcc5f328d9784b8a5ed1ee1631484e7ed9bf247123</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2014</creationdate><topic>Acetochlor</topic><topic>Acids</topic><topic>Analysis</topic><topic>Analytical Chemistry</topic><topic>Atrazine</topic><topic>Biochemistry</topic><topic>Characterization and Evaluation of Materials</topic><topic>Chemistry</topic><topic>Chemistry and Materials Science</topic><topic>Contaminants</topic><topic>Detection limits</topic><topic>Dichlorophenoxyacetic acid</topic><topic>Diuron</topic><topic>Environmental conditions</topic><topic>Environmental Sciences</topic><topic>Equilibrium</topic><topic>Food Science</topic><topic>Herbicides</topic><topic>Laboratory Medicine</topic><topic>Metabolites</topic><topic>Monitoring/Environmental Analysis</topic><topic>Nucleic acids</topic><topic>Optimization</topic><topic>Organic chemicals</topic><topic>Pesticides</topic><topic>Pollutants</topic><topic>Receiving</topic><topic>Research Paper</topic><topic>Samplers</topic><topic>Sampling</topic><topic>Thermodynamic equilibrium</topic><topic>Thermodynamics</topic><topic>Uptakes</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Fauvelle, Vincent</creatorcontrib><creatorcontrib>Mazzella, Nicolas</creatorcontrib><creatorcontrib>Belles, Angel</creatorcontrib><creatorcontrib>Moreira, Aurélie</creatorcontrib><creatorcontrib>Allan, Ian J.</creatorcontrib><creatorcontrib>Budzinski, Hélène</creatorcontrib><collection>PubMed</collection><collection>CrossRef</collection><collection>ProQuest Central 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J.</au><au>Budzinski, Hélène</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Optimization of the polar organic chemical integrative sampler for the sampling of acidic and polar herbicides</atitle><jtitle>Analytical and bioanalytical chemistry</jtitle><stitle>Anal Bioanal Chem</stitle><addtitle>Anal Bioanal Chem</addtitle><date>2014-05-01</date><risdate>2014</risdate><volume>406</volume><issue>13</issue><spage>3191</spage><epage>3199</epage><pages>3191-3199</pages><issn>1618-2642</issn><eissn>1618-2650</eissn><abstract>This paper presents an optimization of the pharmaceutical Polar Organic Chemical Integrative Sampler (POCIS-200) under controlled laboratory conditions for the sampling of acidic (2,4-dichlorophenoxyacetic acid (2,4-
D
), acetochlor ethanesulfonic acid (ESA), acetochlor oxanilic acid, bentazon, dicamba, mesotrione, and metsulfuron) and polar (atrazine, diuron, and desisopropylatrazine) herbicides in water. Indeed, the conventional configuration of the POCIS-200 (46 cm
2
exposure window, 200 mg of Oasis® hydrophilic lipophilic balance (HLB) receiving phase) is not appropriate for the sampling of very polar and acidic compounds because they rapidly reach a thermodynamic equilibrium with the Oasis HLB receiving phase. Thus, we investigated several ways to extend the initial linear accumulation. On the one hand, increasing the mass of sorbent to 600 mg resulted in sampling rates (
R
s
s) twice as high as those observed with 200 mg (e.g., 287 vs. 157 mL day
−1
for acetochlor ESA). Although detection limits could thereby be reduced, most acidic analytes followed a biphasic uptake, proscribing the use of the conventional first-order model and preventing us from estimating time-weighted average concentrations. On the other hand, reducing the exposure window (3.1 vs. 46 cm
2
) allowed linear accumulations of all analytes over 35 days, but
R
s
s were dramatically reduced (e.g., 157 vs. 11 mL day
−1
for acetochlor ESA). Otherwise, the observation of biphasic releases of performance reference compounds (PRC), though mirroring acidic herbicide biphasic uptake, might complicate the implementation of the PRC approach to correct for environmental exposure conditions.
Figure
POCIS and μPOCIS in river media</abstract><cop>Berlin/Heidelberg</cop><pub>Springer Berlin Heidelberg</pub><pmid>24691721</pmid><doi>10.1007/s00216-014-7757-0</doi><tpages>9</tpages><orcidid>https://orcid.org/0000-0001-5282-9011</orcidid><orcidid>https://orcid.org/0000-0003-1028-9154</orcidid></addata></record> |
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subjects | Acetochlor Acids Analysis Analytical Chemistry Atrazine Biochemistry Characterization and Evaluation of Materials Chemistry Chemistry and Materials Science Contaminants Detection limits Dichlorophenoxyacetic acid Diuron Environmental conditions Environmental Sciences Equilibrium Food Science Herbicides Laboratory Medicine Metabolites Monitoring/Environmental Analysis Nucleic acids Optimization Organic chemicals Pesticides Pollutants Receiving Research Paper Samplers Sampling Thermodynamic equilibrium Thermodynamics Uptakes |
title | Optimization of the polar organic chemical integrative sampler for the sampling of acidic and polar herbicides |
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