ASTM D7600-2009e1 0000 Standard Test Method for Determination of Aldicarb Carbofuran Oxamyl and Methomyl by Liquid Chromatography Tandem Mass Spectrometry《液相色谱串联质谱法测定涕灭威 克百威 杀线威及灭多.pdf
《ASTM D7600-2009e1 0000 Standard Test Method for Determination of Aldicarb Carbofuran Oxamyl and Methomyl by Liquid Chromatography Tandem Mass Spectrometry《液相色谱串联质谱法测定涕灭威 克百威 杀线威及灭多.pdf》由会员分享,可在线阅读,更多相关《ASTM D7600-2009e1 0000 Standard Test Method for Determination of Aldicarb Carbofuran Oxamyl and Methomyl by Liquid Chromatography Tandem Mass Spectrometry《液相色谱串联质谱法测定涕灭威 克百威 杀线威及灭多.pdf(10页珍藏版)》请在麦多课文档分享上搜索。
1、Designation: D7600 091Standard Test Method forDetermination of Aldicarb, Carbofuran, Oxamyl andMethomyl by Liquid Chromatography/Tandem MassSpectrometry1This standard is issued under the fixed designation D7600; the number immediately following the designation indicates the year oforiginal adoption
2、or, in the case of revision, the year of last revision. A number in parentheses indicates the year of last reapproval. Asuperscript epsilon () indicates an editorial change since the last revision or reapproval.1NOTEThis Test Method was changed editorially in 2012.1. Scope1.1 This procedure covers t
3、he determination of aldicarb,carbofuran, oxamyl and methomyl (referred to collectively ascarbamates in this test method) in surface water by directinjection using liquid chromatography (LC) and detected withtandem mass spectrometry (MS/MS). These analytes are quali-tatively and quantitatively determ
4、ined by this method. Thismethod adheres to multiple reaction monitoring (MRM) massspectrometry.1.2 This test method has been developed by US EPARegion5 Chicago Regional Laboratory (CRL).1.3 The values stated in SI units are to be regarded asstandard. No other units of measurement are included in thi
5、sstandard.1.4 The Detection Verification Level (DVL) and ReportingRange for the carbamates are listed in Table 1.1.4.1 The DVL is required to be at a concentration at least3 times below the Reporting Limit (RL) and have a signal/noise ratio greater than 3:1. Fig. 1 displays the signal/noiseratios of
6、 the primary single reaction monitoring (SRM) transi-tions and Fig. 2 displays the confirmatory SRM transitions atthe DVLs for the carbamates.1.4.2 The reporting limit is the concentration of the Level 1calibration standard as shown in Table 2 for the carbamates.1.5 This standard does not purport to
7、 address all of thesafety concerns, if any, associated with its use. It is theresponsibility of the user of this standard to establish appro-priate safety and health practices and determine the applica-bility of regulatory limitations prior to use.2. Referenced Documents2.1 ASTM Standards:2D1129 Ter
8、minology Relating to WaterD1193 Specification for Reagent WaterD2777 Practice for Determination of Precision and Bias ofApplicable Test Methods of Committee D19 on WaterD3856 Guide for Management Systems in LaboratoriesEngaged in Analysis of WaterD3694 Practices for Preparation of Sample Containers
9、andfor Preservation of Organic ConstituentsD5847 Practice for Writing Quality Control Specificationsfor Standard Test Methods for Water AnalysisE2554 Practice for Estimating and Monitoring the Uncer-tainty of Test Results of a Test Method in a SingleLaboratory Using a Control Sample Program2.2 Other
10、 Documents:EPApublication SW-846 Test Methods for Evaluating SolidWaste, Physical/Chemical Methods33. Terminology3.1 Definitions:3.1.1 detection verification level (DVL), na concentrationthat has a signal/noise ratio greater than 3:1 and is at least 3times below the reporting limit (RL).3.1.2 report
11、ing limit (RL), nthe concentration of thelowest-level calibration standard used for quantification.3.1.3 carbamates, nin this test method, aldicarb, carbo-furan, oxamyl and methomyl collectively.1This test method is under the jurisdiction of ASTM Committee D19 on Waterand is the direct responsibilit
12、y of Subcommittee D19.06 on Methods forAnalysis forOrganic Substances in Water.Current edition approved Dec. 1, 2009. Published February 2012. DOI: 10.1520/D7600-09E01.2For referenced ASTM standards, visit the ASTM website, www.astm.org, orcontact ASTM Customer Service at serviceastm.org. For Annual
13、 Book of ASTMStandards volume information, refer to the standards Document Summary page onthe ASTM website.3Available from National Technical Information Service (NTIS), U.S. Depart-ment of Commerce, 5285 Port Royal Road, Springfield, VA, 22161 or at http:/www.epa.gov/epawaste/hazard/testmethods/ind
14、ex.htm.1Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.3.2 Abbreviations:3.2.1 pptparts per trillion, ng/L3.2.2 NDnon-detect4. Summary of Test Methods4.1 This is a performance-based method and modificationsare allowed to improve perf
15、ormance.4.2 For carbamate analysis, samples are shipped to the labbetween 0C and 6C and analyzed within 7 days of collection.In the lab, the samples are spiked with surrogate, filtered usinga syringe driven Millex HV PVDF filter unit and analyzeddirectly by LC/MS/MS.4.3 Aldicarb, carbofuran, oxamyl,
16、 methomyl and 4-bromo-3,5-dimethylphenyl-N-methylcarbamate (BDMC, surrogate)are identified by retention time and two SRM transitions. Thetarget analytes and surrogate are quantitated using the primarySRM transitions utilizing an external calibration. The finalreport issued for each sample lists the
17、concentration of aldi-carb, carbofuran, oxamyl, methomyl and the BDMC surrogaterecovery.5. Significance and Use5.1 The N-methyl carbamate (NMC) pesticides: aldicarb,carbaryl, carbofuran, formetanate hydrochloride, methiocarb,methomyl, oxamyl, pirimicarb, propoxur, and thiodicarb havebeen identified
18、by EPA as working through a common mecha-nism. They affect the nervous system by reducing the ability ofthe enzyme cholinesterase. Cholinesterase inhibition was theprimary toxicological effect of regulatory concern to EPA inassessing the NMCs food, drinking water and residential risks.In most of the
19、 country, NMC residues in drinking watersources are at levels that are not likely to contribute substan-tially to the multi-pathway cumulative exposure. Shallowprivate wells extending through highly permeable soils intoshallow, acidic ground water represent what the EPA believesto be the most vulner
20、able drinking water.45.2 This method has been investigated for use with reagentand surface water for the selected carbamates: aldicarb, carbo-furan, oxamyl and methomyl.6. Interferences6.1 Method interferences may be caused by contaminants insolvents, reagents, glassware and other apparatus producin
21、gdiscrete artifacts or elevated baselines. All of these materialsare demonstrated to be free from interferences by analyzinglaboratory reagent blanks under the same conditions assamples.6.2 All glassware is washed in hot water with a detergent,rinsed in hot water followed by distilled water. The gla
22、sswareis then dried and heated in an oven at 250C for 15 to 30minutes. All glassware is subsequently cleaned with acetone,then methanol.6.3 All reagents and solvents should be pesticide residuepurity or higher to minimize interference problems.6.4 Matrix interferences may be caused by contaminantsth
23、at are co-extracted from the sample. The extent of matrixinterferences can vary considerably from sample source de-pending on variations of the sample matrix.7. Apparatus7.1 LC/MS/MS System7.1.1 Liquid Chromatography (LC) SystemA completeLC system is needed in order to analyze samples.5A systemthat
24、is capable of performing at the flows, pressures, controlledtemperatures, sample volumes and requirements of the stan-dard may be used.7.1.2 Analytical Column-WatersXBridge C18, 150 mm 32.1 mm, 3.5 m particle size, or equivalent.7.1.3 Tandem Mass Spectrometer (MS/MS) SystemAMS/MS system capable of M
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