Ultra-pressure liquid chromatography–electrospray tandem mass spectrometry for multiresidue determination of pesticides in water

A multiresidue analysis method has been developed for the determination of pesticides in water by ultra-performance liquid chromatography (UPLC) combined with tandem mass spectrometry (MS/MS). The selected pesticides represent a broad range of polarity and volatility [benzoylcyclohexanedione (mesotr...

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Veröffentlicht in:Journal of Chromatography A 2008-08, Vol.1202 (2), p.163-172
Hauptverfasser: Gervais, G., Brosillon, S., Laplanche, A., Helen, C.
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creator Gervais, G.
Brosillon, S.
Laplanche, A.
Helen, C.
description A multiresidue analysis method has been developed for the determination of pesticides in water by ultra-performance liquid chromatography (UPLC) combined with tandem mass spectrometry (MS/MS). The selected pesticides represent a broad range of polarity and volatility [benzoylcyclohexanedione (mesotrione and sulcotrione); chloroacetamide (acetochlor, alachlor, dimethenamide, and metolachlor); phenoxyacetic acid (2,4-D and MCPA); phenoxypropionic (dichloprop and mecoprop); phenylurea (chlortoluron, diuron, isoproturon, linuron, and metoxuron); sulfonylurea (foramsulfuron, iodosulfuron, and nicolsulfuron); triazine (atrazine, cyanazine, desethylatrazine (DEA), desisopropylatrazine (DIA), simazine, and terbutylazine)]. The analytes were extracted using solid-phase extraction (SPE). The separation was carried out on an acquity UPLC BEH C18 column (1.7 μm, 50 mm × 1 mm ID) using a gradient elution profile and mobile phase consisting of 0.1% formic acid in water and acetonitrile. The pesticides were detected with a tandem mass spectrometer after being ionised positively or negatively (depending on the molecule) using an electrospray ionisation (ESI) source. To achieve the suitable extraction conditions for sample preparation, several parameters affecting the efficiency of SPE such as the nature of the sorbent and the eluent, extractant volume and pH were studied. The best recovery was obtained by the extraction with an Oasis HLB cartridge and 3 mL of a solution of acetonitrile/dichloromethane (1:1, v/v) at pH 2. The average recoveries of the pesticides in different samples ranged from 82 to 109%. The weight least squares (WLS) linear regression was used to calculate the limits of detection and quantification (LOD and LOQ) because the dispersion was heteroskedastic. All the pesticides could be correctly quantified at a concentration level of 50 ng L −1 and most of them could be detected at a concentration inferior or equal to 8 ng L −1. Efficiency and robustness of this method were evaluated by the analysis of several samples of real natural water.
doi_str_mv 10.1016/j.chroma.2008.07.006
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To achieve the suitable extraction conditions for sample preparation, several parameters affecting the efficiency of SPE such as the nature of the sorbent and the eluent, extractant volume and pH were studied. The best recovery was obtained by the extraction with an Oasis HLB cartridge and 3 mL of a solution of acetonitrile/dichloromethane (1:1, v/v) at pH 2. The average recoveries of the pesticides in different samples ranged from 82 to 109%. The weight least squares (WLS) linear regression was used to calculate the limits of detection and quantification (LOD and LOQ) because the dispersion was heteroskedastic. All the pesticides could be correctly quantified at a concentration level of 50 ng L −1 and most of them could be detected at a concentration inferior or equal to 8 ng L −1. 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The selected pesticides represent a broad range of polarity and volatility [benzoylcyclohexanedione (mesotrione and sulcotrione); chloroacetamide (acetochlor, alachlor, dimethenamide, and metolachlor); phenoxyacetic acid (2,4-D and MCPA); phenoxypropionic (dichloprop and mecoprop); phenylurea (chlortoluron, diuron, isoproturon, linuron, and metoxuron); sulfonylurea (foramsulfuron, iodosulfuron, and nicolsulfuron); triazine (atrazine, cyanazine, desethylatrazine (DEA), desisopropylatrazine (DIA), simazine, and terbutylazine)]. The analytes were extracted using solid-phase extraction (SPE). The separation was carried out on an acquity UPLC BEH C18 column (1.7 μm, 50 mm × 1 mm ID) using a gradient elution profile and mobile phase consisting of 0.1% formic acid in water and acetonitrile. The pesticides were detected with a tandem mass spectrometer after being ionised positively or negatively (depending on the molecule) using an electrospray ionisation (ESI) source. 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purification</topic><topic>Pesticides</topic><topic>Pesticides - analysis</topic><topic>Pesticides - isolation &amp; purification</topic><topic>Pollution</topic><topic>Reproducibility of Results</topic><topic>Solid Phase Extraction</topic><topic>Spectrometry, Mass, Electrospray Ionization - methods</topic><topic>Tandem Mass Spectrometry - methods</topic><topic>ultra-pressure liquid chromatography</topic><topic>UPLC–MS/MS</topic><topic>Water analysis</topic><topic>Water Pollutants, Chemical - analysis</topic><topic>Water Pollutants, Chemical - isolation &amp; purification</topic><topic>water pollution</topic><topic>Water treatment and pollution</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Gervais, G.</creatorcontrib><creatorcontrib>Brosillon, S.</creatorcontrib><creatorcontrib>Laplanche, A.</creatorcontrib><creatorcontrib>Helen, C.</creatorcontrib><collection>AGRIS</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>Hyper Article en Ligne (HAL)</collection><jtitle>Journal of Chromatography A</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Gervais, G.</au><au>Brosillon, S.</au><au>Laplanche, A.</au><au>Helen, C.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Ultra-pressure liquid chromatography–electrospray tandem mass spectrometry for multiresidue determination of pesticides in water</atitle><jtitle>Journal of Chromatography A</jtitle><addtitle>J Chromatogr A</addtitle><date>2008-08-22</date><risdate>2008</risdate><volume>1202</volume><issue>2</issue><spage>163</spage><epage>172</epage><pages>163-172</pages><issn>0021-9673</issn><eissn>1873-3778</eissn><coden>JOCRAM</coden><abstract>A multiresidue analysis method has been developed for the determination of pesticides in water by ultra-performance liquid chromatography (UPLC) combined with tandem mass spectrometry (MS/MS). The selected pesticides represent a broad range of polarity and volatility [benzoylcyclohexanedione (mesotrione and sulcotrione); chloroacetamide (acetochlor, alachlor, dimethenamide, and metolachlor); phenoxyacetic acid (2,4-D and MCPA); phenoxypropionic (dichloprop and mecoprop); phenylurea (chlortoluron, diuron, isoproturon, linuron, and metoxuron); sulfonylurea (foramsulfuron, iodosulfuron, and nicolsulfuron); triazine (atrazine, cyanazine, desethylatrazine (DEA), desisopropylatrazine (DIA), simazine, and terbutylazine)]. The analytes were extracted using solid-phase extraction (SPE). The separation was carried out on an acquity UPLC BEH C18 column (1.7 μm, 50 mm × 1 mm ID) using a gradient elution profile and mobile phase consisting of 0.1% formic acid in water and acetonitrile. The pesticides were detected with a tandem mass spectrometer after being ionised positively or negatively (depending on the molecule) using an electrospray ionisation (ESI) source. To achieve the suitable extraction conditions for sample preparation, several parameters affecting the efficiency of SPE such as the nature of the sorbent and the eluent, extractant volume and pH were studied. The best recovery was obtained by the extraction with an Oasis HLB cartridge and 3 mL of a solution of acetonitrile/dichloromethane (1:1, v/v) at pH 2. The average recoveries of the pesticides in different samples ranged from 82 to 109%. The weight least squares (WLS) linear regression was used to calculate the limits of detection and quantification (LOD and LOQ) because the dispersion was heteroskedastic. All the pesticides could be correctly quantified at a concentration level of 50 ng L −1 and most of them could be detected at a concentration inferior or equal to 8 ng L −1. Efficiency and robustness of this method were evaluated by the analysis of several samples of real natural water.</abstract><cop>Amsterdam</cop><pub>Elsevier B.V</pub><pmid>18644603</pmid><doi>10.1016/j.chroma.2008.07.006</doi><tpages>10</tpages><orcidid>https://orcid.org/0000-0002-9085-7985</orcidid></addata></record>
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subjects Acetonitriles - chemistry
Analysis methods
Analytical chemistry
Applied sciences
Chemical Sciences
Chemistry
Chromatographic methods and physical methods associated with chromatography
Chromatography, High Pressure Liquid - methods
electrospray ionization
Environmental analysis
Exact sciences and technology
herbicide residues
herbicides
Hydrogen-Ion Concentration
liquid chromatography
mass spectrometry
Methylene Chloride - chemistry
multiresidue analysis
Natural water pollution
Other chromatographic methods
pesticide residues
Pesticide Residues - analysis
Pesticide Residues - isolation & purification
Pesticides
Pesticides - analysis
Pesticides - isolation & purification
Pollution
Reproducibility of Results
Solid Phase Extraction
Spectrometry, Mass, Electrospray Ionization - methods
Tandem Mass Spectrometry - methods
ultra-pressure liquid chromatography
UPLC–MS/MS
Water analysis
Water Pollutants, Chemical - analysis
Water Pollutants, Chemical - isolation & purification
water pollution
Water treatment and pollution
title Ultra-pressure liquid chromatography–electrospray tandem mass spectrometry for multiresidue determination of pesticides in water
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